o:?. A i^i O
CEMBER 1993
FORKTA
Durnal of the Oriental Bird Club
OBC Council
Richard Bosanquet (Treasurer)
Steve Broyd (Sales Officer)
Mike Crosby (Membership Secretary)
Will Duckworth
Jonathan Eames (Bulletin Art Editor)
Dick Filby (Meetings Officer)
Daryl Gardner
Nick Gardner (Promotions Officer)
Graeme Green (Sales support)
Richard Grimmett
Rob Innes
Carol Inskipp (Conservation Officer)
Tim Inskipp
Frank Lambert
Nigel Lindsey (Publicity Officer)
Adrian Long (Bulletin Editor)
Nigel Redman (Chairman)
Simon Stirrup (Secretary)
Graham Spinks
Dave Weaver
Editorial Committee
Richard Grimmett, Tim Inskipp ( Forktail Editor), Nigel Redman
OBC Representatives
Paul Andrew (Australia); Prof. K. Z. Husain (Bangladesh); Prof. Yao-kuang Tan
(China); Dr Jiri Mlikovsky (Czechoslovakia); Jesper Madsen and Anders Prieme
(Denmark); Hannu Jannes (Finland); Roland Eve (France); Dr W. Thiede (Germany);
Mike Chalmers and David Melville (Hong Kong); Prakash Gole (India); Derek
Holmes and Bas van Balen (Indonesia); Chris Murphy (Ireland); Dr Carlo Violani
(Italy); Akira Hibi (Japan); Dennis Yong and Mike Chong (Malaysia); Rajendra
Suwal (Nepal); Frank Rozendaal (Netherlands); Terje Axelsen (Norway); Ashiq
Ahmad Khan (Pakistan); Prof. Joey Barrill (Philippines); Lim Kim Seng (Singapore);
Dr Sarath Kotagama and Upali Ekanayake (Sri Lanka); Per Alstrom (Sweden); Dr W.
Suter (Switzerland); Philip Round and Uthai Treesucon (Thailand); Dr Robert
Kennedy (U.S.A.).
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Cover photograph: Slaty-backed Forktail Iznicurus schistacctis> Nepal (see Tyler and Ormerod within). Photo:
'V t ...
1994
1
Raptor migration on Bali, Indonesia . 3
P. M. THOMPSON, W. G. HARVEY, D. L. JOHNSON, D. J. MILLIN,
S. M. A. RASHID, D. A. SCOTT, C. STANFORD and J. D. WOOLNER.
Recent notable bird records from Bangladesh . 13
A. J. GASTON, P. J. GARSON and S. PANDEY.
Birds recorded in the Great Himalayan National Park, Himachal Pradesh, India . 45
S. J. TYLER and S. J. ORMEROD.
The ecology of river birds in Nepal . 59
P. D. ROUND.
Winter records of the Manchurian Reed-Warbler Acrocephalus ( agricola ) tangorum
from Thailand . 83
C. R. ROBSON, J. C. EAMES, NGUYEN CU and TRUONG VAN LA.
Birds recorded during the third BirdLife/Forest Birds Working Group expedition in
Viet Nam . 89
C. INSKIPP and T. P. INSKIPP.
Birds recorded during a visit to Bhutan in spring 1993 . 121
Short communications
A. VITTERY.
The birds of Pakistan: supplementary observations from the northern Punjab and hills . 143
D. G. VRETTOS.
Observations on the breeding of the Palawan Blue-Flycatcher Cyomis lemprieri . 148
P. ALSTROM and U. OLSSON.
Blyth’s Leaf-Warbler Phylloscopus reguloides found breeding in Thailand . 150
R. I. DE SILVA, E. PERERA, L. PERERA and K. SAMARASINGHE.
Black Tern Chlidonias niger. a new species for Sri Lanka . 153
R. I. DE SILVA and L. PERERA.
Long-billed Plover Charadrius placidus : a new species for Sri Lanka . 154
A. LEWIS.
Asian Stubtail Urosphena squameiceps: a new species for Nepal and the Indian subcontinent .. 155
A. LEWIS.
Black-and-yellow Grosbeak Mycerobas icterioides : a new species for Nepal . 156
V. PRAKASH, N. V. PRAKASH and W. S. CLARK.
Oriental Honey-Buzzard Pemis ptilorhyncus: a new species for the Andaman Islands, India. .. 157
R. GREGORY-SMITH.
Golden-spectacled Warbler Seicercus burkii: a new species for Peninsular Malaysia . 158
Guidelines for contributors
159
Forktai] 9
CORRECTIONS TO Forktail 8
The Editorial Committee apologise for a number of errors in Zacharias and
Gaston Birds of Wynaad.
Species incorrectly listed as new for Kerala:
LARGE HAWK-CUCKOO Cuculus sparverioides
RUFF Philomachus pugnax
WHITE STORK Ciconia ciconia
BLACK REDSTART Phoenicians ochruros
TYTLER’S LEAF-WARBLER PhyUoscopus tytleri
See Baker and Inglis (1930).
See Gaston (1979) J. Kerala Nat. Hist. Soc.
See Narayanakurup (1989) J. Bombay Nat. Hist. Soc. 86:
239.
See Namassivayan and Sivaprasad (1981) Newsletter for
Birdwatchers 2 1
See Harrap and Redman (1990) J. Bombay Nat. Hist. Soc.
86: 460-461.
Species incorrectly listed as new breeding records for Kerala:
BROWN-CAPPED WOODPECKER Dendrocopos nanus
BANDED BAY CUCKOO Cacomantis sonneratii
COMMON MOORHEN Gallinula chloropus
BLACK- WINGED KITE Elanus caeruleus
LITTLE CORMORANT Phalacrocorax tiiger
LITTLE EGRET Egretta garzetta
GREAT EGRET Casmerodius albus
INTERMEDIATE EGRET Mesophoyx intermedia
CATTLE EGRET Bubulcus ibis
BLACK-CROWNED
NIGHT-HERON Nycticorax nycticorax
ASIAN BROWN-FLYCATCHER Muscicapa dauurica
See Betts (1934) J. Bombay Nat. Hist. Soc. 37: 197-203.
SeeNeelakantan (\969) Newsletter for Birdwatchers 9(\2): 3.
See Neelakantan (1976) J. Bombay Nat. Hist. Soc. 72: 537.
See Jackson (1971) J. Bombay Nat. Hist. Soc. 68: 107.
See Uthaman (1990) J. Bombay Nat. Hist. Soc. 87: 139.
See Neelankantan (1986) Keralathile Pakshikal.
See Uthaman (1990) J. Bombay Nat. Hist. Soc. 87: 139.
See Uthaman (1990) J. Bombay Nat. Hist. Soc. 87: 139.
See Neelankantan (1986) Keralathile Pakshikal.
See Uthaman (1990) J. Bombay Nat. Hist. Soc. 87: 1 39.
See Jackson (1971)^7. Bombay Nat. Hist. Soc. 68: 112-113.
ISSN 0950-1746
© Oriental Bird Club 1993
Published for the Oriental Bird Club bv
Rubythroat Publications
6 Corinthian Close, Basingstoke
Hampshire RG22 4TN U.K.
Printed on recycled paper by Soloprint, Eaton Socon, U.K.
1994
FORKTAIL 9 (1993): 3-11
3
Raptor migration on Bali, Indonesia
J. S. ASH
An account of visible, mostly high-flying, raptor migration in the autumn of 1990 adds to earlier
information collected in 1982. In 1990 over 1 1,000 raptors on 32 days passed eastwards, comprising
principally Oriental Honey-buzzards Pemis ptilorhyncus and two Asiatic Accipiier species, Chinese
Goshawk A. soloensis and Japanese Sparrowhawk A. gularis. It is presumed that this large passage has
passed through Peninsular Malaysia and the Greater Sundas, and there is evidence to support this from
Malaysia, but virtually none from Indonesia. Their final destination is unknown. These migrants are
accompanied by smaller numbers of other raptors, huge numbers of Fork-tailed Swifts Apus pacificus,
some hirundines and other species.
Following the discovery of an impressive diurnal autumn migration of
raptors through Bali, Indonesia, in late October 1982 (Ash 1984), a return
visit was made in 1990 to obtain more information on the species involved,
their direction of flight, numbers, and possible clues to their ultimate
destination. The same area of observation in north-west Bali was visited in
October and November 1 990, and further observations were made elsewhere
in Bali on subsequent days.
In 1982 raptors, together with large numbers of some other species,
starting each day 2-3 h after sunrise, arrived in north-west Bali from the
direction of Java. They continued on over Bali on an E/ESE course. The main
raptors involved were Oriental Honey-buzzards Pemis ptilorhyncus, Japanese
Sparrowhawks Accipiter gularis and Chinese Goshawks A. soloensis.
Non-raptors in greatest numbers were Fork-tailed Swifts Apus pacificus
and Blue-tailed Bee-eaters Merops philippinus. The species involved consisted
of birds originating in eastern Asia, and most must have passed over Java, and
possibly much of Sumatra, before reaching Bali. Few remain on Bali and
their ultimate destination is unknown.
Evidence from Peninsular Malaysia (Wells 1990a and b) shows there is a
large northerly return passage in the spring across the Malacca Straits.
Presumably included here are birds which travel south through Peninsular
Malaysia in autumn, and perhaps others which have moved south into
Indonesia on other routes. The main species involved in Peninsular Malaysia
are also Oriental Honey-buzzards and sparrowhawks. There seem to be no
other observations on raptor migration throughout the whole of Indonesia,
so that the information from Bali is of considerable interest in demonstrating
the existence of a large, previously unrecognised passage into the eastern
sector (Wallacea) of the archipelago. There are in fact extremely few previous
records at all of these raptors from Bali, and there is no evidence that they
spend their non-breeding season there in any numbers.
4
J. S. ASH
Forktail 9
Counts of over 1 1 ,000 raptors on 32 days in 1990 confirmed that the same
three species which occurred in 1 982 were again the principal ones involved;
that the passage was in good progress, but had not reached its peak by 9
October; that most migration was at a very great height; and that passage was
eastwards to areas for which there was no, or very little, previous knowledge
on the species.
LOCALITY AND METHODS
The observation site used from 9 October - 9 November 1990 was in the
western corner of the beach, close to the fringing mangroves, at T eluk T erima
(8°09’N 114°32’E), in Bali Barat National Park. It provided excellent,
unrestricted views from SW-NW towards Java, on which its prominent
eastern volcanos were clearly visible over the intervening forested hills of
Prapat Agung on Bali. To the north and north-east there were open views
over the bay, and from south-west through south and east the forested
mountainous spine of Bali was conspicuous.
Scattered early morning arrivals of migrants mostly flew low. As thermal
activity increased during the day, so did the height of migration, and many
raptors could be found only by constantly scanning the sky, preferably using
clouds when present for a pale background against which they might be
discerned more easily. Sunrise was within a few minutes of 06h00 local time
throughout. There was only little passage during the first three hours after
sunrise, so that the observers’ time of arrival at the observation site was
planned for c. 08h30. The period between dawn and this time was spent
along the flight route so that any early movement could be seen. Binoculars
of 9x and 10x40 were used constantly by my wife and myself, joined by Victor
Mason during the period 3-9 November, a 30x telescope occasionally, a
compass at times for following flight directions, and large scale compass
direction lines marked out on the beach - along which the flight routes of birds
flying nearby could be sighted.
Identification
With good views there was no great difficulty in identifying the three main
species involved, Oriental Honey-buzzard and the two sparrowhawks. The
latter were often very difficult to separate when flying high, and particularly
when in flocks which were sometimes mixed. Often the only clue that
Chinese Goshawks were present was when the white underwing coverts of a
turning bird caught the sun. For this reason an unknown proportion of the
birds recorded as Japanese Sparrowhawks may have been Chinese Goshawks,
but the figure is probably low, because the ratio of the figures for definite
Japanese Sparrowhawks compared with definite Chinese Goshawks are
1994
Raptor migration on Bali, Indonesia
5
similar to those for the total Japanese Sparrowhawk figures compared with
Chinese Goshawks. It is possible that other similar species, such as Besra
Accipiter virgatus, if they occurred, could have been overlooked. Other
species, including some of uncertain identification, are also discussed in the
species accounts below.
METEOROLOGY
No special facilities were available for recording weather conditions. Normally
the meteorological situation remained fairly constant during the day once a
pattern had become established. The changes which took place, usually due
to increases in thermal activity and unimportant changes in wind strength,
were between 09h00 and lOhOO, more or less coinciding with the onset of
migratory activity. During the 32 days of observation the wind was between
S and W (180 -270 ) on 30 days, of which on 1 8 days it was from 181-225 and
on 12 from 226 -270 . On one day it blew from 175, and on another from 280.
Averaging these figures provides a mean wind vector of approximately 221
(=SW’S). Wind speed assessed on the Beaufort scale varied from force 1-6
with a mean of 3. 1 .
Cloud cover was more difficult to assess, and a subjective mean daily figure
was estimated on a scale of 1-10; values were mainly low and produced a
mean of 2.5, which correctly indicated that generally there was little cloud.
Usually there was more cloud inland over the mountains and less over the sea.
RESULTS
Raptor occurrences
Of over 11,000 raptors counted on 32 days the three species, Oriental Honey-
buzzard, Japanese Sparrowhawk and Chinese Goshawk accounted for
10,945 (99.4%) (Table 1). These, together with the other species noted, are
discussed here:
ORIENTAL HONEY-BUZZARD Pemis ptilorhyncus
A total of 2,186 birds passed on 31 days, 10 October - 9 November. The
largest number was 391 (18% of the total for this species) on 27 October (77/
h). Earliest morning arrivals were at 08h30 and the latest at 14h00, so that
passage was during 2.5 - 8.0 h after sunrise. Peak movement occurred in the
quarter hour period 10hl5-10h30 (4.25-4.50 h after sunrise), when of the
total birds seen 1 2% passed over, and 82.5% of birds were seen 09h 15-1 2h 1 5
(3.25 - 6.25 h after sunrise). 75% of all Oriental Honey-buzzard passage
occurred from 19 October - 3 November.
6
J. S. ASH
Forktail 9
Table 1. Summary of movements of three species, Oriental Honey-buzzard Peniis plilorhyncus, Japanese
Sparrowhawk Accipiter gularis and Chinese Goshawk A soloensis , at Bali Barat, 9 October- 9 November
1990
* There was a second 'A hour period at 10h30-10h45 with similar numbers
[EASTERN MARSH-HARRIER Circus spilonotus
A large brown harrier, brown above and below, with a large white rump, flew
east at 09h50 on 12 October. Possible species were immature Pied Harrier
C. melanoleucos, adult Swamp Harrier C. approximans, or Eastern Marsh-
Harrier. Identification was not determined, but following my experience
with the latter in the breeding season of 1 99 1 this species seems most likely.]
CHINESE GOSHAWK Accipiter soloensis
A total of 924 birds occurred on 31 days, 10 October - 9 November, the
largest number being 189 (20% of the total for this species) on 20 October
(60/h). First arrivals in the morning were at 08hl5 and the latest at 12h30
(2.25-6.50 h after sunrise). Peak movements were in the quarter hours of
09h30-09h45 and 10h30-10h45, when 16% and 17% of the birds seen passed
over, and 83% of birds occurred 08h45-10h30 (2.75-4.50 h after sunset).
79% of Chinese Goshawks occurred from 13-25 October.
JAPANESE SPARROWHAWK Accipiter gularis
This species was greatly in excess of the Chinese Goshawk, in the proportion
1994
Raptor migration on Bali, Indonesia
7
of 8.4: 1 .0, but the latter was more concentrated during the middle part of the
observation period (see below under that species) . As noted already, separation
of these two species was often difficult so that comparisons should be
regarded with caution. A total of 7,835 birds identified as this species made
it the commonest raptor seen, on all 32 days 9 October - 9 November. The
largest number was 1,278 (16% of the total for this species) on 19 October
(3 1 3/h). Earliest morning arrival was at 07h30 and the latest at 1 3h45 (1.50-
7.75 h after sunrise). Peak movement occurred in the quarter hour period
10h00-10hl5 (4.00-4.25 h after sunrise), when 17% of the birds seen flew
over, and 92% of birds passed from 09h30-llh45 (3.30-5.75 h after
sunrise). 73% of all Japanese Sparrowhawks passed from 10-20 October.
GREY-FACED BUZZARD Butastur indicus
Single birds flew east at 10h35 on 27 October, at 10h20 on 31 October, and
at llh35 on 6 November. All showed patterned underparts, unlike the
uniformly pale underparts of the Rufous-winged Buzzard B. liventer, which
is the only other likely species. There is no previous record for Bali, and this
northern breeder is regarded by MacKinnon (1990) as a rare straggler to
Java.
BONELLES EAGLE Hieraaetus fasciatus
A bird flying east at 09hl0 on 14 October agreed with the description of this
species and the many I have seen in Europe and North Africa, including
having long white ‘headlights’ on the leading edges of the wings, and the pale
eyes; however, the underwing coverts were whitish without any indication of
a dark bar.]
RUFOUS-BELLIED EAGLE Hieraaetus kienerii
An immature, moulting into adult plumage, flew east with other migrant
raptors at 08h40 on 26 October. There are two previous records from Bali
(Ash 1 984) . Possibly these are wanderers from Java, where it is apparently a
rare resident (MacKinnon 1990). All sightings at Singapore have been
during raptor passage seasons (Wells 1990b), and there are one or two
records of apparent migrants, or birds accompanying migrants of other
species, in the Malay Peninsula (Dr D. R. Wells in litt. 8 December 1991).
CHANGEABLE HAWK-EAGLE Spizaetus cirrhatus
The following 10 birds were considered at the time to be, with some
misgivings, this species, as they passed through with other eastward flying
migrants: one on 10, 11 and 19 October, two on 18 October and 2
November, and three on 22 October, and other more or less similar birds
were seen. Plumage often resembled that of some Oriental Honey-buzzards,
but flight, wing-shape, and wing position in flight differed, which helped to
distinguish them from this otherwise rather similar species. However, some
individuals with fawn or cinnamon underwings were certainly not Oriental
Honey-buzzards, nor apparently this species either.
8
J. S. ASH
Forktail 9
PEREGRINE FALCON Falco peregrinus
One flew east high at 09h30 on 28 October.
In addition, a few other species were seen: single Ospreys Pandion haliaetus
on 8 days, 1 1 October - 7 November, could have been one or more
individuals based in the area; seven Brahminy Kites Haliastur indus sightings
on six days, 9 October - 8 November, could have been local birds; one or two
White-bellied Fish-Eagles Haliaeetus leucogaster on eight days, 10 October -
6 November, were on a direct flight, presumably from Java; single Black
Eagles Ictinaetus malayensis on four days, 12 October - 9 November, were
presumed to be local birds.
MIGRATORY BEHAVIOUR
The first migrant raptor arrivals in the morning were usually flying low, often
in flapping flight, and had possibly been roosting locally on Bali. Such early
morning activity is unusual, for elsewhere migrant raptors delay take-off until
the onset of thermal activity. Apparently birds crossing the Bali Straits, only
a short distance away to the west and only 2.5 km wide at its narrowest,
awaited thermal activity for assistance. The commencement of thermals was
usually indicated by the sight of birds responding to them, followed a little
later by the appearance of small puffs of white cloud in the sky. On many days
thermal activity soon became intense, enabling birds to ascend very rapidly.
On arrival at or near the top of the thermal they were dashed about in a
spectacular manner among the whirling shreds of cloud, to such an extent as
to provoke some thought about the physical and physiological stresses
involved. Birds often shot out of the top of these thermals like darts, to
continue on their migration in long very fast glides with partly closed wings
towards the next thermal. The whole phenomenon was one of frantic activity,
unlike the generally more leisurely ascent and onward progress of migrant
raptors seen in the Middle East and Africa.
Height of migration
It was difficult to assess the height of flight. Most birds were obviously very
high, and through 1 0x40 binoculars often became invisible against a blue sky.
On Bali, a bird the size of a sparrowhawk could just be seen through 10x40
binoculars at a measured horizontal distance of 4,800 m, and this same bird
is likely to be no less visible overhead against a white cloud. Possibly the
highest detectable birds at Bali Barat were as high as this. Based, largely
subjectively, on watching birds among mountains of known altitudes in
Ethiopia, I estimated at an early stage that the higher birds on Bali may have
been at over 3,000 m. A visiting glider pilot, accustomed to looking at flying
performances in thermals and assessing altitudes, judged that the lower birds
1994
Raptor migration on Bali, Indonesia
9
we saw, before they reached the small white clouds, were at above 1,800 m.
He could only say that the higher birds were obviously considerably higher
than this . V ery often birds were within clouds and were seen either descending
from below them, or appearing in view as the clouds rose above them. At
times flocks of sparrowhawks or long lines of Oriental Honey-buzzards were
seen flying out of clouds. On cloudier days it was never known how many
birds might be passing unseen within clouds and, at other times, how many
might be invisible at extreme vertical range against a blue sky.
Direction of flight
No systematic observations were made, but haphazard observations as time
permitted of individual birds or flocks of birds watched until out of sight
confirmed that they were passing on two divergent routes, broadly eastwards
and south-eastwards (Table 2). Not included in the tabular figures are birds
seen flying off about south-east and then turning eastwards on reaching the
mountains: possibly all the birds on this south-easterly course eventually
turned at the mountains; or otherwise they may have continued along the far
side of the mountains, and some may even have reached the south coast of
Bali. From observations on 10 November, by which time passage was much
reduced at Teluk Terima, at Pulaki (8°09’S 1 14°41’E), where 21 Japanese
Sparrowhawks and two Oriental Honey-buzzards flew east 09h00-10h00,
and at Lovina (8°10’S 1 1 5°02’E) where seven of eight Japanese Sparrowhawks
seen 1 3h20- 1 3h5 5 also flew east, it was clear that at least part of the eastward
stream continued in that direction. A few observations in the south-east of
Bali, including one of four Japanese Sparrowhawks at Ubud (8°31’S 1 1 5°15’E)
on 11-12 November in a direct south-easterly flight, and of six more, two of
which flew north, and one Chinese Goshawk which flew north-east at
Suwung(8°42’S 1 15°14’E) on the south-east coast 14-21 November, suggested
that the south-eastward stream from Teluk Terima may reach south-east
Bali.
Table 2. Flight directions of raptors over Teluk Terima, Bali
10
J. S. ASH
Forkiail 9
DISCUSSION
In 1982 there were observations on seven days, 17-26 October, with a total
of 6 1 5 raptors (Ash 1984). In 1982 and 1990 observations were in the same
area but at different sites. In these years Japanese Sparrowhawks were the
most numerous species with 56% and 71% respectively of the raptor total.
Interestingly, Oriental Honey-buzzards were in similar proportions in the
two years at 19% and 20%, but Chinese Goshawks at 25% in 1982 were
much lower in 1990 at only 8%. In the period 17-26 October in 1990 the
Chinese Goshawk proportion was higher at 14% (645 in a total of 4,614
birds), but still well below the 1982 figure. Whether this indicates a real
reduction in numbers remains to be seen.
The Chinese Goshawk is regarded as an occasional winter visitor to Java,
and is also recorded for Bali, and Japanese Sparrowhawks are regular passage
migrants to Java and Bali, according to MacKinnon ( 1 990) . In fact, there are
no records of Chinese Goshawks as winter visitors to Bali, but there are for
Japanese Sparrowhawks (although perhaps the possible confusion with Besra
has not always been borne in mind) . MacKinnon (1990) also refers to a short-
crested race of Oriental Honey-buzzard occurring as an occasional winter
visitor to Java, but from Bali there are no such records. East of Bali this group
of three migrant species is virtually unknown. All are essentially non-forest
species, so that the rapid deforestation of Java is unlikely to have resulted in
forcing them to proceed further east than they would previously have done.
An eastward flight would take the species concerned into increasingly
savanna-like habitat, not inimitable to any of them. If they proceed as far as
New Guinea, presumably they will be obliged to face much longer and more
frequent sea-crossings than any they would have had to undertake previously
on their journey. It is significant that the only two records of Oriental Honey-
buzzard P. p. orientalis in the Lesser Sundas east of Bali are dated almost a
century ago, from the island of Salayan (6°05’S 120°30’E), south of Sulawesi
in November (Hartert 1896), where it may have been overwintering, and
from the small island of Kisan (8°05’S 127°10’E), north-east of Timor, in
December 1897 (Finsch 1900), where it was presumably over-wintering
(White and Bruce 1986).
It is not known what proportion of the migrating raptors entering Bali
arrive at Bali Barat: possibly others arrive on other routes. The numbers
returning northwards in spring from Sumatra through Peninsular Malaysia,
as measured by observations of Oriental Honey-buzzards at Cape Rachado
(Wells 1990a), are greatly in excess of those found so far in Bali. For example,
Wells found 800+/h Oriental Honey-buzzards returning via the Cape and
counted 2,548 on 6 days in spring between 15 February and 2 April,
compared with the 2,186 in the Bali study in 31 days, 10 October - 9
November (Table 1). The autumn passage must be more protracted than the
1994
Raptor migration on Bali, Indonesia
11
period of observation in Bali suggests. Wells (1990a) reported most intense
passage of Oriental Honey-buzzards in the autumn in Peninsular Malaysia
was throughout October-November, a total of at least 60 days (compared
with the 32 days of observation in Bali).
It is likely that much Japanese Sparrowhawk migration was missed in Bali.
The large number of 700 on 10 October at the start of observations suggests
this was the case, and Wells found that the intense passage of this species
included the last quarter of September extending throughout October.
Further observations are needed from Bali to elucidate the situation.
The main requirements in the future are:
a) continued observations, similar to those at Teluk Terima, should extend
over a longer period from mid-September - mid-November.
b) surveys of the Bali Strait area to investigate the breadth of the raptor flight¬
line.
c) survey of the east coast of Bali, especially at Gunung Seraya (8°23’S
1 15°40’E), to investigate the departure of raptors eastwards.
d) surveys for visible migration in Java, and on islands east of Bali.
e) radar surveys would provide much more information, and should be
investigated by civil air authorities in Indonesia.
A well-organised cooperative group study would be the ideal method for
tackling this highly interesting phenomenon.
My wife accompanied me throughout the survey and helped greatly in spotting passing birds. Victor
Mason also helped in a similar way 3-9 November. Dr David Wells provided much valuable data for
comparison from Peninsular Malaysia, and the following read an early draft of this paper and made
valuable comments for its improvement, for which I thank them: Mrs J. W. Ash, Bas van Balen, Tim
Inskipp, Dr Peter Jones, Victor Mason and Dr D. R. Wells.
REFERENCES
Ash, J. S. (1984) Bird observations on Bali. Bull. Brit. 0m. Club 104: 24-35.
Brown, L. and Amadon, D. (1968) Eagles, hawks and falcons of the world. Feltham: Country Life Books.
Finsch, O. (1900) Systematische uebersicht der Vogel der Siidwest-Inseln. Notes Leyden Mus. 22: 225-
309.
Hartert, E. (1896) An account of the collections of birds made by Mr Alfred Everett in Celebes and on
the islands south of it. Novit. Zool. 3: 148-183.
MacKinnon, J. (1990). Field guide to the birds of Java and Bali. Yogyakarta: Gadjah Mada University
Press.
Mason, V. and Jarvis, F. (1989) Birds of Bali. Berkeley: Periplus Editions.
Wells, D. R. (1990a) Malayan bird report 1982-83. Malayan Nature Journal 43: 1 16-147.
Wells, D. R. (1990b) Malayan bird report 1986-87. Malayan Nature Journal 43: 172-210.
White, C. M. N. (1973) Migrant Pernis apivorus in the Indonesian archipelago. Bull. Brit. Om. Club93:
116.
White, C. M. N. and Bruce, M. D. (1986) The birds of Wallacea. BOU Check-listNo. 7. London: British
Ornithologists’ Union.
J. S. Ash, Godshill Wood, Fordingbridge, Hampshire, SP6 2LR, U.K.
12
J. S. ASH
Forktail 9
1994
FORKTAIL 9 (1993): 12 -44
13
Recent notable bird records from
Bangladesh
PAUL M. THOMPSON, W. G. HARVEY, DAVID L. JOHNSON,
D. J. MILLIN, S. M. A. RASHID, D. A. SCOTT, CRAIG
STANFORD, and JOHN D. WOOLNER
Details are given of 22 species new for Bangladesh which have been recorded since or were consciously
omitted from the most recent checklist (Harvey, 1 990), and one old record of a new species is also given;
further details are given of 37 species new for Bangladesh listed in Harvey (1990); and new information
is given for 88 species which have few records since 1978, or for which there have either been major
changes in known status, or for which there is uncertainty over status. Bangladesh is very densely
populated and natural resources are under severe human pressure. However, recent fieldwork has
shown that the coastal mudflats and wetlands of the eastern delta, the beels and haors (large shallow lakes
and depressions) of the north-east, and the remaining fragments of forest are all important for a number
of bird species, several of which are globally threatened. Many of the species discussed are winter visitors
or altitudinal migrants. Much still remains to be discovered about the status of birds in Bangladesh.
Although there have been a number of publications dealing with the birds of
Bangladesh, many are difficult to obtain, and many of the older species lists
included speculative records or did not detail observations of claimed new
species, which has led to confusion. Compared with many other countries
in the Oriental Region, Bangladesh has attracted few visiting birdwatchers.
However, Bangladesh is of considerable ornithological interest because of its
extensive but heavily used wetlands; its small areas of evergreen forest akin
to those of the nearby Indian hillstates, which in recent years have been closed
to visitors; its diversity of habitats; and its location on the boundary between
South and South-East Asia.
Harvey (1990) summarised the current status of birds in Bangladesh and
included in his list a number of species new for Bangladesh. The purpose of
this paper is to update Harvey’s list with new records since 1990 and to
provide additional information on some of the records he included but which
have not previously been fully documented. Species discussed in this paper
fall into three main categories: species new for Bangladesh in the period
January 1978 to June 1993 (marked with a * if they were listed in Harvey
(1990) and with a ** if they are previously unpublished), species previously
assumed to occur or which had not been recorded for many years before
1978, and species for which major changes in status have been discovered
within this period. In addition, one old record of a species not listed by
Harvey (1990) is given. Details of all records are given for species with up
to five records since 1978, and for those which have been found to be more
frequent general details of status and peak counts are given. It should be
noted that the phrase ‘new species for Bangladesh’ is a broad definition
14
P. M. THOMPSON et al
Forktail 9
AlinagarTea Estate ( Srwiangal , north-east)
25 Arabiakona Beel (Tangua Haor, north-east)
1 Aricha (Brahmaputra, central)
2 Ashuganj (Meghna, north-east)
3 Bahadurabad railhead (Brahmaputra, central)
Balai Haor (near Jokiganj, north-east of Sylhet ; north¬
east)
4 Banderban (Chittagong, south-east)
Bara Haor (25 km north of Sylhet , north-east)
* Barisal (south-centre)
Baroorah Tea Estate ( Srimangal , north-east)
2 Bhairab Bazar (Meghna, north-east)
24 Bhatigaon (Sunamganj, north-east)
* Brahmaputra River (central)
5 Bhavval National Park (central)
Bogi (eastern Sundarbans, south-west)
Char Khiderpur ( Rajshahi , north-west)
1 1 Chatla Beel (Hakaluki Haor, north-east)
* Chittagong (south-east)
* Chittagong Hilltracts (south-east)
* Comilla (east-centre)
* Cox’s Bazar (south-east)
24 Dekhar Haor (Sunamganj, north-east)
* Dhaka (central)
6 Dhal Char (south-west of Monpara, west of Hatiya;
east-centre)
7 Dhaleswari River (central)
Dhangmari ( Sundarbans , south-west)
Dubla island ( Sundarbans , south-west)
8 Durgapur (Mymensingh, central)
Egg Island (south-east of Kochikhali, Sundarbans ;
south-west)
Erali Beel ( Sylhet , north-east)
9 Faridpur (south-centre)
* Ganges (north-west)
10 Habiganj (north-east)
Hail Haor ( Srimangal , north-east)
1 1 Hakaluki Haor (Moulvi Bazar, north-east)
1 1 Haorkhal (Hakaluki Haor, north-east)
26 Harikhola valley (Whvkeong, Teknaf, south-east)
12 Hatiya (east-centre)
Himchari (Cox's Bazar , south-east)
Joydepur (Dhaka, central)
Kaliakoir (Dhaka, central)
13 Kamalgonj Tea Estate (Kamalgonj, north-east)
13 Kamarchera (Rajkandi, Kamalgonj, north-east)
20 Kamlar Char (Nijumdip, east-centre)
14 Kaptai (south-east)
Katka ( Sundarbans , south-west)
Katka Khal (Kochikhali Tiger Reserve, Sundarbans,
south-west)
1 5 Kawadighi Haor (Moulvi Bazar, north-east)
Khagra ( Sylhet , north-east)
Khakra Kuri Beel (Balai Haor, Sylhet , north-east)
* Khulna (south-west)
Madhabpore Lake ( Srimangal , north-east)
16 Madhapkhundo waterfall (New Samanbagh Tea
Estate, Dhakshinbagh, north-east)
26 Madhya Nhila (Teknaf, south-east)
15 Maijeil Haor (north-east of Kawadighi Haor; north¬
east)
15 Majherbanda Beel (Kawadighi Haor, Moulvi Bazar,
north-east)
Malumghat (Chittagong, south-east)
25 Matian Haor (near Tangua Haor, north-east)
17 Mawa (Padma, central)
18 Meda Beel (Kalamakando, Netrakona, central)
* Meghna River (north-east/east-centre)
19 Modhupur Forest (central)
9 Moulvi Bazar (north-east)
12 Moulvi Char (Hatiya, east-centre)
26 Muchoni (Teknaf, south-east)
* Mymensingh (central)
16 New Samanbagh Tea Estate (Dhakshinbagh, north¬
east)
20 Nijumdip (east-centre)
Nilkamal (Sundarbans, south-west)
21 Noakhali Coast (east-centre)
Nurjahan Tea Estate (Srimangal, north-east)
* Pabna (north-west)
* Padma River (central)
Palangkhali (45 km south-east of Cox's Bazar, south¬
east)
25 Pana Beel (south of Tangua Haor, north-east)
Panerchara (Cox 's Bazar, south-east)
25 Pasua Beel (Gurmar Haor, north-east)
Patenga (Chittagong, south-east)
1 1 Pingla Beel (Hakaluki Haor, north-east)
13 Rajkandi Forest (Kamalgonj, north-east)
15 Rajnagar Tea Estate (Moulvi Bazar, north-east)
* Rajshahi (north-west)
5 Rathura (Bhavval National Park, central)
25 Rauar Beel (Tangua Haor, north-east)
25 Sanir Haor (east of Pasua Beel, north-east)
27 Satcheri Reserve Forest (Telepara, north-east)
27 Sathgao Reservoir (near Satcheri, north-east)
1 3 Shamshernagar Tea Estate (Kamalgonj, north-east)
26 Shilkhali (Teknaf, south-east)
14 Sitapchar Reserve Forest (Kaptai, south-east)
8 Someswari River (near Durgapur, Mymensingh,
central)
22 Sonargaon Town (central)
1 2 Sonar Char (near Monapara and Hatiya , east-centre)
South Halishahar (Chittagong, south-east)
* Srimangal (north-east)
23 St Martin’s Island (south-east)
24 Sunamganj (north-east)
* Sundarbans (south-west)
* Sylhet (north-east)
25 Tangua Haor (north-east)
26 Teknaf (south-east)
27 Telepara (north-east)
28 Thakurgaon (north-west)
Tiger Point (Sundarbans, south-west)
29 Urir Char (east-centre)
West Bhanugach Reserve Forest (Srwiangal, north¬
east)
26 Whvkeong (Teknaf, south-east)
1994
Recent notable bird records from Bangladesh
15
Figure 1 . Bangladesh showing locations mentioned in text.
Locations shown by name are indicated with a *; locations given a number are indicated by that number; remaining
locations are near or within the italicised named location.
16
P. M. THOMPSON el al.
Forktail 9
because in many cases previous lists, for example Rashid (1967), included
species which were assumed to occur but for which specimens or documented
observations were not available. Hence even some species not noted here as
new for Bangladesh may be the first fully documented records.
The information reported is derived largely from an updating of Harvey’s
list by J.D.W. in 1992, and from subsequent observations. It reflects the
dedication of a small but growing band of birdwatchers active in Bangladesh.
The records reported here are all sight records, but are by reliable observers,
and where possible field notes have been collated and are stored with
W.G.H., D.L.J. and P.M.T. The appendix provides a key to observer’s
initials. Records are related to regions of Bangladesh in the following list; this
is a revised version of the regions in Harvey (1990) and the boundaries are
shown in Figure 1 , along with the locations of the 1 07 sites mentioned in the
text. Place names follow current usage in official documents and maps in
Bangladesh, but it should be noted that there are often alternative
transliterations in common usage.
NEW SPECIES AND NOTABLE RECORDS
RAIN QUAIL Cotumix coromandelica A rare or local resident. Although first
recorded from Faridpur by Cripps (1878) and subsequently included in a
number of lists, there is only one recent record - a pair in scrub close to forest
at Malumghat between Chittagong and Cox’s Bazar in the south-east on 26
November 1989 (D.L.J. ).
BLUE-BREASTED QUAIL Cotumix chinensis Presumably a rare resident,
first recorded near Dhaka in the 1 9th century (Simson 1882). There are only
two recent records: a pair were flushed several times in a field of legumes by
the Padma near Mawa, south of Dhaka, on 28 February 1986 (D.A.S.); and
a pair were flushed from marshy grassland at Chatla Beel, Hakaluki Haor in
the north-east on 30 April 1992 (D.A.S., S.M.A.R.).
RUFOUS-THROATED PARTRIDGE Arborophila rufogularis Presumably
a rare resident. Weston (1914) gave the first records from the Sylhet (north¬
east) region. The only recent record is of two birds (photographed) which
had been trapped by hunters in Rajkandi Forest (north-east) in January 1 99 1
(S.M.A.R.).
INDIAN PEAFOWL Pavo cristatus Presumed now extinct. Although first
recorded from north of Mymensingh (central) in the 1 9th century (Godwin-
Austen 1870), the last and only recent record is of one heard calling on the
night of 18-19 March 1986 at Rathura, west of Bhawal National Park
(central) (S.M.A.R.).
**GREATER WHITE-FRONTED GOOSE Anser albifmns Vagrant. One
on a char in the Brahmaputra south of Aricha in December 1982 (A.M.K.)
1994
Recent notable bird records from Bangladesh
17
is the only record for Bangladesh of a species which is a rare winter visitor to
India, but has been recorded in Assam (Ali and Ripley 1987).
FALCATED DUCK A nasfalcata Scarce winter visitor. Since the first - one
shot in greater Sylhet District (Savage 1970) - it appeared that this species
was very rare in Bangladesh. One was shot on the Padma River (central) in
1980 and one was at Sathgao Reservoir in the north-east in 1987 (A.M.K.);
a male was at Pana Beef) Tangua Haor in Sunamganj district in the north¬
east on 2 March 1992 (D.A.S., S.M.A.R.); and a male was in a mixed flock
of about 70 wintering ducks on a char in the Brahmaputra just off the
Bahadurabad railhead (central) on 7 March 1992 (D.L.J., R.H.). However,
following three at Tangua Haor on 3 December 1992 and six there on 3
January 1 993 (S.M.A.R.), an unprecedented 39 were found at the same site
on 27 January 1993 (P.M.T., R.A.); three were also seen at Chatla Beel
(north-east) on 1 February 1993 (S.M.A.R.). This species is listed as a rare
winter visitor in Assam, but is regular in small numbers further west in India
(Ali and Ripley 1 987) and appears to also be a regular visitor in Bangladesh.
RED-CRESTED POCHARD Netta rufina Local winter visitor. Although
Harvey (1990) only admitted a record by R.K. (Khan 1982), there are a
number of historic records, of which the first is by Cripps (1878). However,
recent observations have shown it to be much more numerous than was
previously thought. After one was shot on the Meghna river (east-centre) on
30 November 1986 (A.M.K.), this species has been reported by several
observers in recent winter wildfowl counts. In the north-east the first records
were from four sites in the Tangua Haor complex on 2 March 1992, with a
total of 87 birds (D.A.S., S.M.A.R.). Other sites in the region that winter
were: Someswari River (one male on 22 April 1992) and Pasua Beel (two
pairs on 24 April 1992) (D.A.S.). However, in winter 1992-1993
unprecedented totals were recorded at four sites, only peak counts are given:
300 at Pana Beel on 3 December 1992 (S.M.A.R.), 4002 at Pasua Beel on
3 December 1 992 (S.M.A.R., A.K.), 300 at Haorkhal on 2 1 December 1 992
(S.M.A.R.), and 875 at Tangua Haor on 27 January 1993 (P.M.T., R.A.).
In the central region the only record is of four males and 10 females 6 km
north of Bahadurabad on the Brahmaputra on 7 March 1992 (D.L.J., R.H.).
BAER’S POCHARD Aythya baeri Winter visitor. First listed for Bangladesh
by Rashid (1967), and subsequently recorded in small numbers by several
observers during mid-winter wildfowl counts (for example, a male on Dhaka
Zoo lake in early 1988, W.G.H.). However, it was only during the winters
of 1991-92 and 1992-93 that internationally important numbers of this
threatened species (Collar and Andrew 1988) were discovered wintering in
the north-east of Bangladesh. In February-March 1992 a total of 697 was
recorded, the majority (660) being on Pana Beel, Tangua Haor; but with 27
others at four sites within the Tangua-Pasua complex and 10 at two sites in
Hakaluki Haor (D.A.S., S.M.A.R.). In January-February 1993 a total of
18
P. M. THOMPSON et al.
Forktail 9
1712 was recorded, all from sites where they had been recorded in the
previous winter: 700 at Chatla and Pingla Beels (Hakaluki Haor), 600 at
Pasua Beel, 300 at Haorkhal (Hakaluki Haor), and 112 at Tangua Haor
(S.M.A.R., P.M.T., A.K.).
GREATER SCAUP Aythya marila Rare winter visitor. The only recent
records are of three males and two females with a flock of Tufted Ducks
Aythyafuligiila at Pana Beel, Tangua Haor in the north-east on 2 March 1 992
(D.A.S., S.M.A.R.), one male at the same site on 27 January 1993 (P.M.T.),
and one male at Pasua Beel also on 27 January 1993 (S.M.A.R.). This scarce
winter visitor to the Indian sub-continent may have been overlooked in the
past; Ripley (1982) noted it as occurring in Bangladesh.
COMMON GOLDENEYE Bucephala clangula Vagrant. Weston (1914)
shot one in the winter of 1 9 1 3- 1 9 1 4, a record that was overlooked by Harvey
(1990).
COMMON MERGANSER (GOOSANDER) Mergus merganser Rare
winter visitor. Harvey ( 1 990) noted that this species had not been recorded
since a 19th century record from Sylhet District (Hume, 1888). However,
a pair were observed at Bahadurabad railhead on the Brahmaputra (central)
on 7 March 1992 (D.L.J., R.H.). There are virtually no large fast flowing
rivers in Bangladesh which this species might favour.
**MANDARIN DUCK Aix galericulata Vagrant. The first record for
Bangladesh was of a male seen among a flock of about 200,000 duck at Pasua
Beel (north-east) on 27 January 1993 (S.M.A.R., A.K.). Previous records of
this species from the Indian Sub-continent are specimens from Assam and
Manipur (Ali and Ripley 1987); and one on the lower Arun in Nepal
(Gardiner, 1991).
YELLOW-LEGGED BUTTONQUAIL Tumix tanki Possibly a rare
resident or vagrant. Although listed for Chittagong by Blanford (1898) and
Ali and Ripley (1987), there is only one recent record. One was closely
observed when it flew onto the lawn of a bungalow at Baroorah Tea Estate,
Srimangal (north-east), on 12 April 1987 (D.J.M.).
GREY-CAPPED WOODPECKER Dendrocopos canicapillus and BROWN-
CAPPED WOODPECKER D. nanus The status of these two species,
particularly D. nanus, in Bangladesh requires clarification and further critical
study. Harvey (1990) lists D. canicapillus as the common small woodpecker
in Bangladesh, including in mangroves, and notes D. moluccensis (nanus) as
a rare? resident or visitor, with only one confirmed record - in the remnants
of Tarap Hill Reserve Forest (north-east) on 18 January 1985 (D.J.M.).
However, D. nanus is widespread in the lowlands and plains of the Indian
sub-continent (Ali and Ripley 1987), whereas D. canicapillus is primarily
found in hill forests such as the Himalayan foothills; this status was implied
in Ali and Ripley (1987) for Bangladesh. These two small woodpeckers do
not appear to be common in Bangladesh. Recent observations suggest that
1994
Recent notable bird records from Bangladesh
19
D. nanus may be present in the Sundarbans: two pairs thought to be of this
species were noted in mangroves at Katka and a pair at Nilkamal all in
February 1987 (D.A.S.), but detailed notes were not taken. However, a male
D. canicapillus was closely observed near Katka on 16 December 1988
(W.G.H., D.J.M.). A number of detailed observations in Modhupur forest
(central), including nesting in February 1989, indicate that D. canicapillus is
relatively common there in mixed sal and evergreen forest (W.G.H., D.L.J.,
P.M.T.), and this species has also been recorded several times from West
Bhanugach Reserve Forest and nearby tea estates in the north-east (W.G.H.,
D.L.J., P.M.T.).
PALE-HEADED WOODPECKER Gecinulus grantia Rare resident. First
listed by Rashid (1967), and recorded from the Chittagong Hilltracts
(Husain 1968; Husain and Haque 1976). The only recent record is of one
in primary evergreen forest, which has since been cleared, at Kamarchera,
Rajkandi (north-east) on 22 February 1985 (D.L.J.).
HEART-SPOTTED WOODPECKER Hemicircus canente Vagrant?
Although listed for Bangladesh in Rashid (1967), and Ali and Ripley (1987),
there is only one recent record: one on shade trees near the Tea Research
Institute, Srimangal (north-east) in May 1984 (S.M.A.R.).
GREAT HORNBILL Buceros bicomis Vagrant. Although included in
several lists for Bangladesh since Rashid (1967), the only recent record is of
one flying over West Bhanugach Reserve Forest (Srimangal, north-east) in
February 1990 (F.S., P.D.A.).
BLYTH’S KINGFISHER Alcedo Hercules Vagrant. Although noted for
Sylhet by Ripley (1982) and Ali and Ripley (1987), there is only one recent
record of this threatened species (Collar and Andrew 1988). One was
observed at Hail Haor (north-east) on 22 February 1 985 (D.J.M.), and there
was also a probable record from a nearby tea estate at that time (P.L.W.). It
seems likely that this bird had wandered from the nearby hill states.
RUDDY KINGFISHER Halcyon coromanda Status uncertain: rare resident
or winter visitor. Although listed for Bangladesh by Rashid (1967), Ripley
(1982) and Ali and Ripley (1987), the only recent record is of one well seen
perched along a narrow creek in freshwater mangrove forest near Dhangmari
in the Sundarbans (south-west) on 16 December 1990 (D.A.S.).
* LARGE HAWK-CUCKOO Cuculus sparverioides A rare winter visitor
(and possibly passage migrant), not noted for Bangladesh in Ali and Ripley
(1987) or Ripley (1982). The only records are from West Bhanugach
Reserve Forest (Srimangal) in the north-east where singles were seen on: 13
March 1985 (D.L.J., D.J.M., M.S., P.L.W.), 14 February 1986 (D.J.M.,
P.M.T.), 1 6 January 1 987, 1 5 January 1 988 and 4 March 1 988 (all D.J.M.);
and from the nearby Kamalgonj Tea Estate on 26 December 1992 (D.L.J.,
J.O’M., P.M.T.). A common summer visitor to the Himalayas, this species
may be overlooked in forests at lower altitudes in winter.
20
P. M. THOMPSON el al.
Forktail 9
HODGSON’S HAWK-CUCKOO Cuculus fugax Vagrant? Although
reported as occurring in Bangladesh by Rashid ( 1 967), Ali and Ripley ( 1 987)
and Ripley (1982), the only documented record is of one in a suburban
Dhaka garden on 15-18 October 1987 (W.G.H.).
^ORIENTAL CUCKOO Cuculus saturatus A rare migrant which may occur
more often but identification has only been attempted when birds were
calling. Although included in Rashid (1967), the only record for Bangladesh
is of one watched calling repeatedly in West Bhanugach Reserve Forest
(Srimangal, north-east) on 26 March 1981 (D.L.J.).
*LESSER CUCKOO Cuculus poliocephalus A rare migrant which may occur
more often. Although included in Rashid (1967), the only confirmed records
are: one calling in West Bhanugach Reserve Forest (Srimangal, north-east)
on 23 March 1984 (D.L .J.), one watched closely near Hail Haor, Srimangal
on 22 October 1988 (W.G.H.), and one calling at south Patenga (Chittagong,
south-east) on 21 April 1990 (D.L.J.).
VIOLET CUCKOO Chrysococcyx xanthorhynchus Rare resident or migrant?
Although listed by Rashid (1967), the only confirmed records appear to be:
a sub-adult male in West Bhanugach Reserve Forest (Srimangal, north-east)
on 27 March 1 986 (D.L.J., N.B., R.H.); a male at the same site on 9 January
1987 (D.J.M.), a pair and a single male at the same site in May 1989
(W.G.H.); and a male in Satcheri Reserve Forest (north-east) on 4 May 1992
(D.A.S.).
^HIMALAYAN SWIFTLET Collocalia brevirostris A rare winter visitor
from higher altitudes. First recorded in October 1985 at Baroorah Tea
Estate, Srimangal, north-east (DJM), where it was observed with Asian
Palm-Swifts Cypsiurus balasiensis\ subsequently there was one in January
1986 and two on 7 November 1988 at the same site (D.J.M.). Other records
are of ‘several’ over the River Meghna at Ashuganj (north-east) on 4
November 1988 (D.J.M.), one hawking for insects at Nilkamal in the
Sundarbans (south-west) on 23 March 1 99 1 (D.A.S.), and two over stubble
fields near Khagra, east of Sylhet (north-east) on 25 January 1993 (P.M.T.).
*FORK-TAILED SWIFT Apus pacificus An irregular winter visitor or
passage migrant. The first record is of one hawking insects with Asian Palm-
Swifts Cypsiurus balasiensis near the beach at Cox’s Bazar, south-east, on 12
August 1981 (D.L.J.). Subsequent records are: a large flock over Rangamati
(south-east) in December 1986 (V.Z.); about 3,000 on 27 April 1988 over
Cox’s Bazar (P.M.T.); a heavy movement to the north and east over
Srimangal (north-east) on 19 November 1988 (D.J.M.); one over the
Botanical Gardens, Dhaka after a cyclone on 1 December 1988 (W.G.H.);
100+ over forest at Malumghat (near Chittagong) moving north on 27
November 1 989 (D.L.J.); and 1 00+ over Patenga, Chittagong, on 7 December
1991 (D.L.J., P.M.T.). Several of the observations appear to be associated
with storms or cyclones.
1994
Recent notable bird records from Bangladesh
21
CRESTED TREESWIFT Hemiprocne coronata Vagrant. Although listed
for Bangladesh by Rashid (1967) and Khan (1982), there are only two recent
records of this species, which is widely distributed in India. A flock of at least
30 were watched at Bhawal National Park on 1 April 1 979 (D.L.J.), and one
was observed at Madhya Nhila near T eknaf (south-east) in November 1983
(S.M.A.R.).
[ROCK EAGLE-OWL Bubo bengcilensis Status uncertain, listed by Rashid
(1967) but no confirmed record. The record given in Harvey (1990) of one
heard in West Bhanugach Reserve Forest (Srimangal) on 30 March 1987 is
now regarded as probable only.]
DUSKY EAGLE-OWL Bubo coromandus A rare resident. Since the 19th
and early 20th centuries (Tytler 1 854, Bates 1 935) there appear to have been
only five records of this species in Bangladesh, although it is widespread in
wooded areas of the Indian sub-continent. Apart from one in West
Bhanugach Reserve Forest (Srimangal) on 1 8 November 1 989 (D.L.J.), it is
only known from Modhupur Forest (central) . At the latter site one was found
on 27 April 1990, a pair were closely observed and tape-recorded on 15
December 1990 (D.L.J., N.B.), a pair were observed copulating on 6
November 1992 (D.L.J., R.H., N.B., A.W.), and a pair were observed at the
same location on 22 January 1993 (D.L.J., P.M.T.).
TAWNY FISH-OWL Ketupa flavipes Rare resident? Although listed by
Rashid (1967) and Ripley (1982) for the hills of Bangladesh, the only recent
records are of one in woodland near New Samanbagh Tea Estate (north¬
east) on 17 January 1990 (D.L.J.), and one closely observed for about 30
minutes while it bathed in a small pool and then dried out in Modhupur
Forest (central) on 8 December 1992 (J. & S.O’M.).
*BROWN WOOD-OWL Strix leptogrammica A rare resident. Only
recorded in Modhupur Forest (sal forest). Following unconfirmed reports
from 1976 (per R.K.), one was found to be resident near Joloi resthouse
during 1 987 and 1 988 (C.S.), and subsequently the only records are of: two
found roosting in the crown of a sal tree on 6 January 1990 (D.L.J., N.B.,
R.H.); one watched eating a rat and calling (tape-recorded) on 22 January
1993 (D.L.J., P.M.T.); and one calling on 9 April 1993 (D.L.J.).
GREAT EARED-NIGHTJAR Eurostopodus macrotis A rare or localised
resident. Although listed by Rashid ( 1 967) and Ripley ( 1 982) for Bangladesh,
the only confirmed records are from Modhupur Forest (central) where they
were in display flight/song in February 1989 (W.G.H.), and from New
Samanbagh T ea Estate (north-east) on 1 1 and 1 2 November 1990 when up
to 20 were observed leaving forest and hawking for insects over tea plantations
and paddyfields (D.L.J.).
PALE-CAPPED PIGEON Columba punicea Rare, status uncertain. First
listed for what is now Bangladesh by Blanford (1898). However, the only
recent records are of 2-3 perched high in trees in the evening on three dates:
22
P. M. THOMPSON ei al
Forktail 9
14 May 1988, 22 October 1988, and 20 February 1989; all in West
Bhanugach Reserve Forest, Srimangal in the north-east (W.G.H.). It seems
likely that this threatened species (Collar and Andrew 1988) had wandered
from the nearby hill states where it is known from Assam and Manipur (Ali
and Ripley 1987).
**PIN-TAILED GREEN-PIGEON Treron apicauda Rare, possibly a
nomad from neighbouring hills. Although not listed by Harvey (1990), this
species was listed for Bangladesh by Rashid (1967), Husain (1979), Khan
(1982), and Ali and Ripley (1987). However, the only documented record
is of a party of six watched closely feeding in the canopy in West Bhanugach
Reserve Forest (Srimangal, north-east) on 2 1 February 1 992 (D.A.S., A.K.).
It seems unlikely that this species might be resident, since this is the best
watched forest in Bangladesh; but it is partly nomadic depending on food
supplies and is known from the nearby hill ranges of Assam (Khasi, Cachar),
Nagaland and Manipur (Ali and Ripley 1987).
**WEDGE-T AILED GREEN-PIGEON Treron sphenura Rare, possibly a
nomad from neighbouring hills. Although not listed by Harvey (1990), this
species was listed for Bangladesh by Rashid (1967), Khan (1982), and Ali
and Ripley (1987). The only documented record is of a party of six feeding
in the canopy of a tall fruiting tree in Satcheri Reserve Forest, Telepara
(north-east) on 10 March 1992 (D.A.S., S.M.A.R.). It seems' likely that
these had wandered from higher altitudes because, like T. apicauda, this
species occurs through the Himalayan foothills and is known from Nagaland
and the hills of Assam (Ali and Ripley 1987).
SARUS CRANE Grus antigone Former resident?. Although first recorded
from the Dhaka area in the 19th century (Simson 1882), the only recent
records are: reports of a pair in Thakurgaon (north-west) up to 1 989 (per
S.M.A.R.); one shot at an unknown location in the north-east in 1990
(specimen in Bangladesh National Museum); and a captive bird of the
eastern subspecies G. a. sharpii at Teknaf (south-east) on 1 1 February 1991
(S.M.A.R.). The last bird may well have come from Myanmar.
DEMOISELLE CRANE Grus virgo Rare winter visitor or vagrant.
Although included in Husain (1979) and a number of other lists, the only
confirmed record appears to be one associating with egrets Egretta in fields
near Bhatigaon, south-west of Sunamganj (north-east) in January 1986
(S.M.A.R.).
MASKED FINFOOT Heliopais personata Rare visitor or resident? Although
listed by Rashid (1967) and subsequent authors for the Sundarbans, there
have been only four recent records. One was seen in a small channel near
Tiger Point in the Sundarbans (south-west) on 29 January 1 984 (D.L.J.); the
remaining three records are all from Katka Khal in Kochikhali Tiger Reserve
in the Sundarbans: two in March 1984 (S.M.A.R.), four in May 1986
(S.M.A.R.), and one on 8 February 1987 (S.M.A.R., D.A.S.).
1994
Recent notable bird records from Bangladesh
23
**LITTLE CRAKE Porzana parua Vagrant. There are only two previous
records of this species from the Indian subcontinent (Ali and Ripley 1987).
On 25 December 1991 a male and female were closely watched swimming
and walking among emergent vegetation in the middle of Hail Haor in the
north-east (P.M.T., D.L.J.).
WOOD SNIPE Gallinago nemoricola Rare winter visitor. Although listed for
Bangladesh by Rashid (1967) and Ali and Ripley (1987), there is only one
recent record of this threatened species (Collar and Andrew 1 988). One was
flushed at close range from a stream in dense forest in West Bhanugach
Reserve Forest, Srimangal (north-east), on 22 December 1992 (D.L.J.).
This species is an altitudinal migrant from the Himalayas, but there is limited
suitable forest habitat in Bangladesh.
**SWINHOE’S SNIPE Gallinago megala Scarce winter visitor? The only
record is of two found with both Common and Pintail Snipe (G. gallinago and
G. stenura ) at Hail Haor (north-east) on 23 February 1992 (D.A.S.). They
were identified from G. stenura on the basis of larger size, heavier flight,
longer bills, more conspicuous white in the outer tail, and call. Rashid ( 1 967)
assumed that this species would occur in Bangladesh, and it has been
recorded from neighbouring Assam, Manipur and West Bengal (Ali and
Ripley 1 987) . The difficulties of field identification mean that it has probably
been overlooked.
JACK SNIPE Lymnocryptes minimus Scarce winter visitor. First recorded
from Faridpur (south-central) by Cripps (1878) and from Sylhet by Eden
(1881). The only recent records of this species are of one shot at Hail Haor
(Srimangal, north-east) in March 1990, and subsequently one wintering
along a stream in a tea estate at Srimangal and a few others wintering at Hail
Haor. It would appear to be a regular but scarce and local winter visitor to
the north-east, where it has been recorded from 27 September in all months
through to March during 1990-91 (all records J.D.W.).
*BAR-TAILED GODWIT Limosa lapponica A scarce winter visitor,
previously overlooked but regular in small numbers in coastal areas. The first
record was a total of 19 from the area around Hatiya (east-centre) during
mid-winter wildfowl counts in January 1989 (Bakewell and Howes 1989,
Scott and Rose 1 989) . Subsequently recorded in each January wildfowl and
wader count in the east-centre (14 in 1990, 31 in 1991, 1 in 1992, and 6 in
1 993; M.A.B., A.K., S.M.A.R., P.M.T.). At Patenga (south-east) it has
been recorded in August, September, December, January and March,
usually as single birds, but with a maximum of 1 4 on 1 1 January 1 990 (D.L.J.,
W.G.H.) . There is only one record away from the coastal zone: two near Hail
Haor (north-east) on 2 February 1993 (S.M.A.R.).
*FAR EASTERN CURLEW Numenius madagascariensis The only record,
and first for the Indian subcontinent is of one on 27 November 1 988 at Cox’s
Bazar, south-east (H. & C.L.). The closest previous records of this long-
24
P. M. THOMPSON et al.
Forktail 9
distance migrant from east Asia are from Malaysia and Thailand where it is
a rare passage migrant (King et al. 1975, Boonsong and Round 1991).
**SPOTTED REDSHANK Tringa erythropus Although Rashid (1967)
anticipated that it was a winter visitor to much of Bangladesh, this species was
not listed by Harvey (1990). First recorded by Mountfort and Poore (1968),
who recorded 13 in the Sundarbans on 24 and 26 November 1967.
Subsequently few claims (Husain et al. 1 983, van der Ven 1 988) until one in
the north-east in January 1990 (P.D.A. and F.S.). Records during 1991-2
indicate that there may have been an influx that winter and that it is a not
uncommon winter visitor. Most have been recorded from the north-east: one
at Hail Haor on 25 December 1 99 1 (P.M.T., D.L.J.); 1 5 on flooded fields
near Hakaluki Haor on 27 December 1 99 1 (P.M.T., D.L.J.); a total of 1 35
during surveys in February-March 1 992 (D.A.S.) - these were concentrated
at Pasua Beel (55), Haorkhal (30), and Majherbanda Beel (30); and 18
during a repeat survey in April-May 1992 with 13 at Pingla Beel (D.A.S.,
S.M.A.R.). Away from the haors of the north-east, 22 were on Sonar Char
near Hatiya (east-centre) on 1 8 January 1 992 (P.M.T., A.K., A.W.A.), and
about 30 were along the Brahmaputra north of Aricha also on 18 January
1992 (D.L.J.).
NORDMANN’S GREENSHANK Tringa guttifer Scarce winter visitor.
Although noted as a rare winter visitor by Husain (1979) and Ali and Ripley
(1987), there are few confirmed records of this threatened species (Collar
and Andrew 1988). Apart from an exceptional 300 at Nijumdip, Hatiya
(east-centre) in January 1988 (S.M.A.R.), in subsequent mid-January wildfowl
and wader counts there are totals of only three, one and two respectively in
1989, 1990 and 1991 from the eastern delta (A.W.A., D.B., J.H., S.M.A.R.).
This species has also been recorded in small numbers from Patenga
(Chittagong, south-east): a total of eight sightings - probably fewer birds -
during two weeks in January 1 988 (V.Z.); and two in January 1 990, one on
8 March 1990, and two on 3 January 1991 (allD.L.J.). Away from the coast
a flock of 25 was reported from Chatla Beel (Hakaluki Haor, north-east)
during a cold spell on 2 December 1992 (S.M.A.R.).
*GREY-TAILED TATTLER Tringa brevipes Vagrant. The first record for
the Indian Sub-continent, and Bangladesh, was of two at Patenga near
Chittagong (south-east) on 18 May 1989 (D.L.J.). They were closely
observed both on the mudflats and in flight, with the following characters
noted: sandplover sized with long straight dark bills and yellowish legs, plain
grey uppersides with white eye-stripe, white belly and barred or scaly neck,
breast and flanks. In flight uppersides all grey with rump and tail paler grey,
double-noted call with each note inflected upward at the end. The closest
previous records are from Thailand where it is a rare passage migrant
(Boonsong and Round 1991).
1994
Recent notable bird records from Bangladesh
25
*GREAT KNOT Calidris tenuirostris A scarce or irregular passage migrant
and winter visitor. Although listed by Rashid (1967), the first confirmed
record was of up to 1 00 at Patenga (Chittagong, south-east) in October 1 987
(V.Z.), this has since proved to be the main site so far discovered for the
species in Bangladesh. Subsequently recorded at Patenga on 1 5 occasions
between peak counts of 50+ on 27 October 1 988 (W.G.H.) and over 1 20 on
29 August 1992 (D.L.J., P.M.T.). However, none was recorded there during
visits between September 1990 and May 1992 (D.L.J.). Away from this site
it has only been rarely recorded: one at South Halishahar beach (Chittagong)
on 26 May 1988 (DJM); singles in 1989 and 1992 during January wildfowl
counts on islands in the eastern delta; 15 at Egg Island on the edge of the
Sundarbans on 5 February 1 990 (D.L.J.); and five at Urir Char (east-centre)
on 13 January 1993 (P.M.T., S.M.A.R., A.K.).
*RED KNOT Calidris canutus A rare winter visitor only recorded in 1989.
The ‘first record’ from Hatiya Island (east-centre) in January 1 989 (Bakewell
and Howes 1 989; Scott and Rose 1 989), has since been found to be an error
(D. Bakewell pers. comm, to D.A.S.). The only records, therefore, are all
from Patenga (Chittagong, south-east) and all in 1 989; it seems likely that the
same group of birds were involved: 20 on 10 April (W.G.H.), 5 on 20 April
(D.L.J.), four in breeding plumage on 18 May (W.G.H.), and 13 on 1
December (D.L.J.).
SPOON-BILLED SANDPIPER Eurynorhynchus pygmeus Despite being
first recorded from Chittagong, south-east, (three specimens) in the mid
1 9th century (Blyth 1 857), it was only in 1 989 that it was discovered that this
threatened species (Collar and Andrew 1988) is a regular winter visitor and
that Bangladesh is probably the main wintering ground for this species.
Totals during January counts carried out as part of the coordinated Asian
Mid-winter Wildfowl counts have been: three in 1988, 257 in 1989, 45 in
1991, about 100 in 1992, and two in 1993 (A.W.A., D.B., M.A.B., J.H.,
A.K., S.M.A.R., P.M.T.). The main sites for this species are in the eastern
side of the delta (east-centre) particularly Hatiya Island, Urir Char and the
Noakhali Coast, and Dhal Char on the outer edge of the delta. In addition
it has been regularly recorded in small numbers at Patenga (south-east): no
more than three have been recorded at one time, but a total of 1 8 ‘bird-days’
have been recorded on 12 occasions between October 1987 and September
1992 covering seven months: August through to November, January, April
and May (W.G.H., D.L.J., P.M.T., V.Z.) . There is also one record from Egg
Island on the edge of the Sundarbans: 4 on 24 February 1992 (D.L.J.). The
coastal chars are a dynamic system and so the sites suitable for this species
(which prefers a substrata of mixed sand and mud) can change within the
space of a year. There may well be other suitable sites and the pattern of
migration is unknown.
26
P. M. THOMPSON el al.
Forktail 9
EURASIAN OYSTERCATCHER Haematopus ostralegus Vagrant? Although
Stanford (1937, 1954) reported a breeding occurrence of this species in the
Sundarbans (south-west), there are only two recent records: one at Nilbaria
north-east of Dubla island on the edge of the Sundarbans in March 1984
(S.M.A.R.), and two at the same site on 9 February 1987 (S.M.A.R.,
D.A.S.).
LONG-BILLED PLOVER Charadrius placidus Vagrant. Although first
listed for Bangladesh by Rashid (1967) there are only two traceable records.
Two were found at a coastal site on Nijumdip (east-centre) on 19 January
1991 (M.A.B.); and one was watched on ploughed fields near Hail Haor,
Srimangal, on 1 January 1991 (J.D.W.). The record given in Harvey (1990)
from May 1978 is now regarded as probable only.
*CRAB PLOVER Dromas ardeola Vagrant. The only record is of six at
Kamlar Char, Nijumdip in the east-central coastal area on 18 January 1988
(S.M.A.R.). The closest locations where it has been regularly recorded are
in Peninsular Thailand (Boonsong and Round 1991) and western India and
Sri Lanka (Ali and Ripley 1987).
* PARASITIC JAEGER (ARCTIC SKUA) Stercorarius parasiticus Vagrant.
The only record is of one on 20 January 1981 in the Swatch of No Ground
off the Sundarbans in Bangladesh Territorial Waters - R.K. (Harvey, 1990).
The nearest previous records are in the Arabian Sea (Ali and Ripley 1987)
and coastal Thailand (Boonsong and Round 1991).
*BLACK-NAPED TERN Sterna sumatrana Vagrant. The only record is of
one in November 1986 towards Moheshkhali island, north of Cox’s Bazar,
south-east (V.Z.). The nearest part of its regular range is the Andaman
Islands (Ali and Ripley 1987).
*EGYPTIAN VULTURE Neophron percnopterus Vagrant. Although
included in Husain (1979), the only confirmed record is of one over Char
Khiderpur near Rajshahi (north-west) on 10 April 1984 (S.M.A.R.).
**EURASIAN GRIFFON Gyps fulvus Vagrant. Two immatures feeding
on a carcass with White-rumped and Long-billed Vultures ( Gyps bengalensis
and G. indicus ) east of Bhairab Bazar in the north-east on 18 February 1992
appear to be the first confirmed record. They were readily distinguished on
size and plumage from the accompanying species. Despite a number of
references to this species in papers on the birds of Bangladesh, for example
Rashid (1967), Mountfort and Poore (1968) and Husain (1979), there is no
specific reference to its occurrence in Bangladesh in Ali and Ripley (1987)
and the species was not listed by Harvey (1990). This species is, however,
an occasional non-breeding visitor to the plains of northern India east to
Assam and south to 20"N (Ali and Ripley 1987), hence its occurrence in
Bangladesh is not unexpected.
*CINEREOUS VULTURE Aegypius monachus Vagrant. Although listed
in Khan (1982), the only documented record is of one in Comilla zoo (east-
1994
Recent notable bird records from Bangladesh
27
centre) in 1987 which had reportedly been captured locally (Harvey 1990).
SHORT-TOED SNAKE-EAGLE Circaetus gallicus Rare winter visitor.
Although first listed for Bangladesh by Rashid (1967) there are only three
recent records: one over Modhupur Forest (Joloi resthouse) in November
1986 (C.S.), two over Himchari, Cox’s Bazar (south-east) on 23 November
1988 (H. & C.L.); and two over Dhaka golf course on 12 December 1992
(D.L.J.).
NORTHERN HARRIER Circus cyaneus Rare winter visitor. Although
Bates ( 1 935) recorded this species from the Chittagong area, it was not listed
in Ripley (1982). There have been several recent records: a male at Baroorah
Tea Estate (near Srimangal) on 16 February 1987 (D.J.M.); a male near
Srimangal in February 1988 (V.Z.); a male on Egg Island in the south-eastern
Sundarbans on 4 February 1 990 (D.L .J.); single males recorded at Hail Haor
in the north-east on 18 January and 30 November 1991 (J.D.W.); a male on
Moulvi Char, Hatiya Island, (east-centre) on 15 January 1992 (P.M.T.); a
male at Hail Haor in December 1992 (D.L.J., J. & S.O’M.); and a male at
Erali Beel (north-east) on 29 January 1993 (S.M.A.R.).
MONTAGU’S HARRIER Circus py gar gus Vagrant. This species was listed
for Faridpur District by Cripps (1878), which may be the source for inclusion
in subsequent lists. There is only one recent record: a male was seen flying
over cultivated fields in Harikhola valley at Whykeong (near Teknaf, south¬
east) in December 1983 (S.M.A.R.).
^NORTHERN GOSHAWK Accipiter gentilis Vagrant. Although listed by
Khan ( 1 982) there are only two documented records: one was watched flying
over a hilltop close to Teknaf (south-east) on 9 December 1983 (S.M.A.R.);
and one was watched for about 10 minutes flying over Dhaka zoo on 23
October 1987 (P.M.T.).
*LONG-LEGGED BUZZARD Buteo rufinus A scarce winter visitor.
Although listed by Khan (1982), the first documented record is of one near
Pabna (north-west) on 30 January 1982 (D.L.J., N.B., R.H., G.F.).
Subsequent records are of: one at Cox’s Bazar (south-east) in November
1987 (H. & C.L.), one flying over the Dhaleswari river near Dhaka on 31
January 1992 (D.L.J., A.M.K., P.M.T., J.D.W.), and one near Bahadurabad
railhead on the Brahmaputra (central) on 5 December 1992 (D.L.J., R.N.,
A.W., N.B.). This species appears to favour sandbanks in the main rivers.
IMPERIAL EAGLE Aquila heliaca Rare winter visitor. Although listed in
Ali and Ripley (1987), the only recent records are: a second year at Uttara,
Dhaka on 4 March 1978, one at Dhaka airport on 16 December 1979, one
at Pabna on 30 January 1 982 (all D.L.J.), two immatures an Teknaf (south¬
east) on 3 December 1 988 (H. & C.L.), and one 6 km north of Bahadurabad
railhead perched on a char in the Brahmaputra (central) on 5 December 1 992
(D.L.J., R.N., A.W., N.B.).
28
P. M. THOMPSON ei al.
Forktail 9
**BONELLI’S EAGLE Hieraaetus fasciatus Vagrant. Although listed for
Bangladesh by Khan ( 1 982) possibly on the basis of a claim by Husain et al.
(1974), the only confirmed record appears to be of one over Satcheri Reserve
Forest, Telepara (north-east) in March 1990 (F.S., P.D.A.). This was
presumably a vagrant from the Himalayas.
*BOOTED EAGLE Hieraaetus pennatus A scarce winter visitor or passage
migrant, Rashid ( 1 967) and Ali and Ripley (1987) presumed that it occurred
but gave no specific records. The first record was a light phase bird over
Kaliakoir (50 km north of Dhaka) on 22 October 1978 (D.L.J.). Subsequent
records are: one 50 km north of Joydepur (central) on 28 April 1 979 (D.L.J.);
a light phase at Modhupur Forest (central) on 15 April 1987 (W.G.H.); a
light phase roosting at Dhaka Zoo on 7 November 1987 (W.G.H.); three at
Dhaka Zoo (two dark phase and one light phase) on 1 2 May 1 988 (W.G.H.,
D.J.M., J.D.W.); a light phase near Mymensingh (central) and another near
Sylhet (north-east) in February 1989 (W.G.H.); one over a grass fire south
of Srimangal in February 1990 (J.D.W.); and one at Patenga (Chittagong)
on 5 April 1990 (D.L.J.).
**SAKER FALCON Falco cherntg Presumably a vagrant, the closest area
where it is regularly recorded, as a scarce winter visitor, is in central Nepal
(Inskipp and Inskipp 1991). The only record is of one well watched resting
and flying in a grassy area near Modhupur Forest (central) on 1 8 April 1 992
(D.L.J., J. & S.O’M.).
GREAT CO RMO RANT Phalacrocorax carbo Local winter visitor. Harvey
(1990) reported no recent records, although this species has appeared in
many past bird lists for Bangladesh (Rashid, 1967) and the oldest record is
that of Lister (1951). However, surveys in 1992/93 revealed that it is still a
winter visitor in moderate numbers to the deeper beels of the Haor Basin in
the north-east, and to the northern reaches of the Brahmaputra River. In the
north-east 54 were recorded from 1 1 sites in February-March 1 992, but only
one was recorded in a survey of the same areas in April-May 1 992 (S.M.A.R.,
D.A.S.). In winter 1992-1993 higher numbers were recorded in the same
region, peaks for the most important sites were: 45 at Pana Beel 27 January
1993 (A.K., S.M.A.R., P.M.T.), 130 at Pasua Beel in November 1992
(S.M.A.R.), and 95 at Sanir Haor on 4 November 1992 (S.M.A.R.); the
majority of records are from the T angua, Matian and Gurmar Haor complexes.
In addition three pairs were found along 6 km of the Brahmaputra river north
of Bahadurabad railhead on 7 March 1992 (D.L.J., R.H.), and a total of 32
in two flocks at the same site on 5 December 1992 (D.L.J., R.N., A.W.,
N.B.).
*PACIFIC REEF-EGRET Egretta sacra Vagrant. There appear to be three
records for Bangladesh, but the species has not been recorded elsewhere on
the mainland Indian subcontinent (Ali and Ripley 1987). Khan (1985)
reported it from St Martin’s Island in the extreme south-east but full details
1994
Recent notable bird records from Bangladesh
29
were not included. Rashid and Khan (1987) likewise reported it from
Teknaf: apparently a number of dark phase birds were seen on mudflats near
Teknaf (south-east) in December 1983 (S.M.A.R., A.K.). Most recently, a
white phase bird was seen on several occasions at Patenga, Chittagong in
January and February 1989 (W.G.H., D.L.J., Harvey 1990). This species
occurs on the Andaman Islands (Ali and Ripley 1 987), and along the Arakan
coast of Myanmar which is adjacent to the Teknaf-St Martin’s region
(Smythies 1986).
GOLIATH HERON Ardea goliath Vagrant. This primarily Afrotropical
species was first recorded in Bangladesh in Khulna District in the south-west
(Prater 1 926); the specimen is held by the Bombay Natural History Society
(Abdulali 1968). There are only two recent records: one flying north at
Himchari Beach, Cox’s Bazar (south-east) on 23 November 1988 (H. &
C.L.), and one well seen while flying over Dhaka Zoo on 20 December 1992
(J. & S.O’M.). It is unknown whether these are recent longdistance vagrants
or have been surviving within the region for some time.
WHITE-BELLIED HERON Ardea insignis Vagrant? This globally
threatened species (Collar and Andrew 1988) was reported to occur in
Bangladesh by Ali and Ripley (1987) and Ripley ( 1 982), but there is only one
well documented or recent observation. A pair were flushed twice from the
forest-lined shore of Madhabpore lake, near Srimangal, on 25 March 1 988,
good views were obtained of both birds in flight (D.J.M.). This species may
have wandered from one of the Indian hillstates.
GREAT BITTERN Botaurus stellaris Rare winter visitor. Although listed
for Bangladesh by Rashid (1967) and Ripley (1982), there are only three
recent records. One was watched flying over Baroorah Tea Estate, Srimangal
(north-east) in September 1 984 (D.J.M.); one flying over marshes at Khakra
Kuri Beel, Balai Haor in the north-east on 6 March 1992 (D.A.S.), and one
flushed from paddy fields at Haorkhal (north-east) on 30 January 1993
(S.M.A.R.).
**BLACK STORK Ciconia nigra Rare winter visitor. The first three records
for Bangladesh are given, although the species was listed as potentially
occurring by Rashid ( 1 967) . One was at Palangkhali on the Naf river south¬
east of Cox’s Bazar (south-east), in December 1983 (S.M.A.R.). Two were
closely observed for eight hours on a low muddy char (sandbank) in the
Brahmaputra River about 3 km north of Aricha (central region) on 18
January 1992, mostly feeding alone but also associating with a flock of 40
Grey Herons Ardea cinerea (D.L.J., R.H., A.W.). One on a char in the
Brahmaputra 6 km north of Bahadurabad railhead on 5 December 1992
(D.L.J., R.N., A.W., N.B.). This species winters sparsely in the Indian
subcontinent so its occurrence is not surprising, although Ripley (1982)
noted it to be absent south of Assam.
30
P. M. THOMPSON el al.
Forktail 9
BLUE PITTA Pitta cyanea A rare summer visitor. Although listed for
Bangladesh by Rashid (1967) and others, the only recent record is from West
Bhanugach Reserve Forest, Srimangal (north-east), in May-June 1988,
where breeding was suspected (Harvey 1990).
NORTHERN SHRIKE Lanius excubitor Rare winter visitor. Although first
recorded from Lalmai, Comilla in the east-centre (Collins 1948), the only
recent record is of one at Ranikong, Durgapur, north of Mymensingh
(central) on 14 February 1984 (S.M.A.R.).
RED-BILLED MAGPIE Urocissa erythrorhyncha Rare winter visitor.
Although included in Rashid (1967), the only recent records are: two at
Muchoni near Teknaf (south-east) in October 1983 (S.M.A.R.) and one in
flight in West Bhanugach Reserve Forest (Srimangal, north-east) in November
1985 (D.J.M., E.F.G.).
SCALY THRUSH Zoothera dauma Vagrant. Although listed for Bangladesh
in Rashid (1967) and Ripley (1982), there is only one recent record. One was
seen in Modhupur Forest (central) on 15 December 1990 (D.L.J.).
DARK-SIDED THRUSH Zoothera marginata Vagrant. Although listed in
Rashid (1967) and Ali and Ripley (1987), there is only one recent record of
one watched down to 1.5 m around a walkway and clump of bamboos on the
Bangladesh Agricultural University campus, Mymensingh (central) on 10
November 1988 (W.G.H.).
TICKELL’S THRUSH Turdus unicolor Vagrant. Although noted from
Bangladesh by Rashid (1967) and Mountfort and Poore (1968), there are
only three recent records. A male was by a homestead wood and pond in a
village between Gopalganj and Barisal (south-centre) on 25 February 1979
(D.L.J.); one was in Bhawal National Park (central) on 27 February 1986
(D.A.S.); and two were seen separately feeding in Modhupur Forest (central)
on 10 February 1989 (W.G.H.).
*WHITE-COLLARED BLACKBIRD Turdus albocinctus Vagrant. A male
in song in Modhupur Forest (central) on 10 February 1989 (W.G.H.) during
a cold spell is the only record, much below its normal altitudinal range.
However, Ali and Ripley ( 1 987) give nearby Meghalaya and Cachar (Assam)
as part of the wintering range.
**GREY-WINGED BLACKBIRD Turdus boulboul Vagrant. There are
only two, previously unpublished, records. A male was seen in thick scrub
in West Bhanugach Reserve Forest (north-east) on 25 March 1978, and a
female was seen at the same site on 13 March 1985 (both records D.L.J.).
The closest part of the wintering range given by Ali and Ripley (1987) is
Cachar in Assam.
**EURASIAN BLACKBIRD Turdus merula Vagrant. The only record is
of a male in Modhupur Forest (central) during a cold spell in January 1982
(S.M.A.R.). Although Ali and Ripley (1987) note it as a winter visitor to the
plains of India, there appears to have been no previous record in Bangladesh.
1994
Recent notable bird records from Bangladesh
31
EYEBROWED THRUSH Turdus obscurus A rare passage migrant. Although
listed by Rashid (1967) and Ali and Ripley (1987), there are only two recent
records: one in West Bhanugach Reserve Forest (north-east) on 14 March
1986 (D.J.M.), and one in coastal woodland at Patenga (south-east) on 7
April 1990 (D.L.J.).
*DUSKY THRUSH Turdus naumanni Vagrant. Although listed by Rashid
(1967), the only confirmed record is of a male closely observed in a belt of
Casuarina trees along the coast at Cox’s Bazar (south-east) on 25 March
1989 (D.L.J.). Ali and Ripley (1987) give this species as a passage migrant
in the north-eastern hillstates.
*LESSER SHORTWING Brachypteryx leucophrys A rare winter visitor.
The first record for Bangladesh was a female caught in a mist-net in West
Bhanugach Reserve Forest (north-east) on 20 February 1986 (D.L.J.). The
only other records are from the same site: at least two which were closely
observed on 20 November 1987 (D.J.M.), and one on 20 February 1989
(W.G.H.). These were presumably altitudinal migrants from the north-east
Indian hillstates, Ali and Ripley (1987) give a lowest altitude of 1500 m.
DARK-SIDED FLYCATCHER Muscicapa sibirica Rare passage migrant.
Although listed in Rashid (1967), the only recent records of this hill species
are of: one in Modhupur Forest (north-centre) on 5 November 1986
(S.M.A.R.), two adults and an immature closely observed in Modhupur
Forest on 9 November 1 99 1 (D.L.J., N.B.), and one in homestead trees near
Erali Beel east of Sylhet (north-east) on 27 April 1992 (D.A.S.).
RUFOUS-GORGETED FLYCATCHER Ficedula strophiata Rare winter
visitor. Although listed as a winter visitor in the Chittagong region (Ali and
Ripley 1987), the only recent record is of one in Modhupur Forest (central)
in December 1988 (C.S.).
*SNOWY-BROWED FLYCATCHER Ficedula hyperythra Rare winter
visitor. The only confirmed records of this species are of a female feeding in
dense cover near the ground in West Bhanugach Reserve Forest (Srimangal,
north-east) on 23 February 1985 (D.L.J.), and a pair in undergrowth at the
same site on 20 and 21 February 1987 (D.J.M.). Ali and Ripley (1987) give
a lowest altitude of 300 m and list it for the nearby hillstates.
ULTRAMARINE FLYCATCHER Ficedula superciliaris Rare winter
visitor. Although listed by Rashid ( 1967), the only recent record is of one on
the edge of forest in Sitapchar forest near Kaptai (south-east) during winter
1987-88 (V.Z.).
^SAPPHIRE FLYCATCHER Ficedula sapphira Vagrant?. The only record
is of a sub-adult male in the understorey of West Bhanugach Reserve Forest
(Srimangal, north-east) on 21 February 1986 (D.L.J., D.J.M.). At about 35
m above sea level this is much lower than the range given by Ali and Ripley
(1987) who state that it occurs in the nearby hillstates seasonally down to
800 m.
32
P. M. THOMPSON et al.
Forktail 9
*SMALL NILTAVA Ni/tava macgrigoriae Vagrant. The only confirmed
record of this species is of a female closely observed while feeding in the
understorey of West Bhanugach Reserve Forest (Srimangal, north-east) on
23 February 1 985 (D.L.J., N.B.). This species might be expected to be more
frequent since Ali and Ripley (1987) note that it breeds in the Garo and Khasi
hills of Meghalaya and winters in the foothills and plains of the Brahmaputra
valley.
RUFOUS-BELLIED NILTAVA Niltava sundara Rare winter visitor. Ali
and Ripley (1987) list it for the Chittagong Hilltracts, but the only recent
records of this skulking species are of one in West Bhanugach Reserve Forest
(north-east) in October 1 987 (C.S.) and a male at Madhapkhundo waterfall,
New Samanbagh Tea Estate (north-east) on 17 January 1990 (D.L.J.).
**FIRETHROAT Luscinia pectardens Vagrant. A male in full breeding
plumage was found in dense woodland at Pasua Beel, Gurmar Haor (north¬
east) on 24 April 1992 (D.A.S., S.M.A.R.), the bird was inquisitive, giving
excellent views, and on several occasions it uttered short bursts of sub-song.
This constitutes the first record for Bangladesh and only the second for the
Indian subcontinent; the first being in January 1950 from the Garo Hills of
Meghalaya, adjacent to Bangladesh (Koelz 1954, Ali and Ripley 1987).
Soon after the Bangladesh record, on 21 June 1992, a pair was seen in the
Mehao Wildlife Sanctuary, Arunachal Pradesh (Katti 1992). This species
is apparently mainly resident in China, breeding from south-east Tibet north
through Sichuan to south-west Kansu and Shensi (Meyer de Schauensee
1984).
INDIAN BLUE ROBIN Luscinia brunnea A rare winter visitor. Although
listed for Bangladesh in Ali and Ripley (1987), the only recent record is of a
female in undergrowth in West Bhanugach Reserve Forest (north-east) on 28
February 1991 (P.M.T.). This species is a regular altitudinal migrant with
part of the population migrating to southern India in the winter.
* RUFOUS-BREASTED BUSH-ROBIN Tarsiger hyperythrus Vagrant.
First record: a female watched down to 1 m feeding on leaf mould in dense
forest in West Bhanugach Reserve Forest (north-east) on 21 October 1988
(W.G.H.). A scarce Himalayan species which makes seasonal altitudinal
movements, and is noted from the Indian hill states in winter (Ali and Ripley
1987).
BLUE-FRONTED REDSTART Phoenicurus frontalis Vagrant from the
Himalayas. Although listed for Bangladesh in Rashid (1967) and Ali and
Ripley (1987), there is only one recent record of one at Sonargaon town
(central) on 29 December 1984 (S.M.A.R.).
*WHITE-CAPPED WATER-REDSTART (RIVER CHAT) Chaimarromis
leucocephalus A rare winter visitor normally found at higher altitudes. Apart
from an undated record in West Bhanugach Reserve Forest (C.S.), this
1994
Recent notable bird records from Bangladesh
33
species has only been recorded from Madhapkhundo waterfall in New
Samanbagh Tea Estate (north-east) where it was first recorded on 31 January
1986 (D.J.M.); subsequently it has been recorded there in most years from
November to February (D.L.J., J.D.W., P.M.T., J. & S.O’M.). It
would appear to be a regular winter visitor to this location at about 100 m
above sea level.
*WHITE-TAILED ROBIN Cinclidium leucurum A rare breeding resident.
Not listed for Bangladesh in Ali and Ripley (1987) or Ripley (1982). First
recorded on 25 March 1978 (D.L.J.). All records are from West Bhanugach
Reserve Forest (north-east) where it is regularly recorded (many observers)
during winter (November to March) . However, on 1 7 June 1988 a recently
fledged juvenile (dark brown with heavy pinkish spotting and the same tail
pattern as an adult) was found (D.J.M., J.D.W.). At 35 m above sea level this
record is much lower than its normal breeding range of above 1200 m (Ali
and Ripley, 1987).
SLATY-BACKED FORKTAIL Enicurus schistaceus Rare visitor? Although
noted for Bangladesh by Rashid (1967) and Ali and Ripley (1987), there are
only two recent records: one in Alinagar Tea Estate (north-east) on 3 May
1985 (D.J.M., P.L.W.), and a pair at Madhapkhundo Waterfall (New
Samanbagh Tea Estate, north-east) on 24 December 1992 (D.L.J., J. &
S.O’M.).
WHITE-CROWNED FORKTAIL Enicurus leschenaulti Rare visitor?
Although noted for Bangladesh in Ali and Ripley (1987) the only recent
record is of two along a stream in West Bhanugach Reserve Forest (north¬
east) on 8 December 1989 (J.D.W.).
**PURPLE COCHOA Cochoa purpurea Vagrant. Although included in
Rashid ( 1 967), the only confirmed record is of an adult male closely watched
at Dhaka Golf Course, at low altitude (under 5 m) and out of its normal forest
habitat, on 2 November 1990 (D.L.J., J.D.W.). This most unlikely of
records was presumably a vagrant from Meghalaya or another of the nearby
hill states, where its altitudinal range is given as 1 000-3000 m (Ali and Ripley
1987). The chances of it being an escape seem very low, and in any case most
cage birds in Bangladesh are caught locally.
WHITE-TAILED STONECHAT Saxicolaleucura Vagrant? Although first
recorded in the 1 9th century from the Garo hills (central-north-east) in what
is now Bangladesh (Godwin-Austen 1870), there is only one recent record
of a male in paddyfields by the road to Banderban (south-east) on 20 April
1990 (D.L.J.).
JERDON’S BUSHCHAT Saxicola jerdoni Rare winter visitor. Although
first recorded in the 19th century from the Garo hills (central-north-east) in
what is now Bangladesh (Godwin-Austen 1870), there are only three recent
records. A male was present at Baroorah Tea Estate (Srimangal, north-east)
34
P. M. THOMPSON et at.
Forktail 9
during February 1985 (D.J.M., E.F.G.), a female was present at exactly the
same place during February 1986 (D.J.M., P.M.T.); and a male was in
extensive grassland at Bara Haor (north-east) on 4 December 1992 (S.M.A.R.,
A.K.).
*DESERT WHEATEAR Oenanthe deserti Vagrant or rare winter visitor.
There are only two records, both from Patenga, Chittagong (south-east) : one
in December 1987 (V.Z.), and a male on the seawall on 7 December 1991
(P.M.T., D.L.J.). The closest area where the species is regularly recorded is
in north-central Nepal (Inskipp and Inskipp 1991).
ROSY STARLING Stumus roseus Rare winter visitor. Although listed by
Rashid (1967), there are only two recent records: one at Patenga, Chittagong
(south-east) in January 1988 (V.Z.), and three (including an adult in good
plumage) in homestead trees east of Kawadighi Haor, near Moulvi Bazar
(north-east) on 22 February 1992 (D.A.S.).
COMMON STARLING Stumus vulgaris Rare winter visitor. Although
listed by Rashid (1967), there are only three recent records, all from Patenga,
Chittagong (south-east): three in December 1987 (V.Z.), 12 on 11 January
1990 (D.L.J.), and at least 20 in recently harvested fields on 7 December
1991 (D.L.J., P.M.T.).
[BEAUTIFUL NUTHATCH Sitta formosa Possible vagrant, listed by
Rashid (1967) but no other records. The record given in Harvey (1990) is
now regarded as probable only.]
WIRE-TAILED SWALLOW Hirundo smithii Vagrant. Although listed for
Bangladesh by Rashid (1967) and others, the only recent record is of two over
the Agricultural University campus at Mymensingh (central) in October
1988 (Harvey 1990).
STRIATED SWALLOW Hirundo striolata Resident? Although listed by
Husain (1979), the only confirmed records appear to be from near Srimangal
(north-east) in November 1988 and March 1989 (W.G.H.). This species has
probably been overlooked in the past among Red-rumped Swallows Hirundo
daurica.
** STREAK-THROATED SWALLOW Hirundo fluvicola Vagrant. The
only record for Bangladesh is of one, watched closely with Barn Swallows
Hirundo rustica for comparison, over a small pond in the East Wildlife
Sanctuary near Katka in the Sundarbans (south-west) on 1 7 December 1 990
(D.A.S.). According to Ali and Ripley (1987) this species has not previously
been recorded from Bangladesh, Bengal, or Assam; however, northern
populations are migratory so a vagrant in Bangladesh is not unexpected.
**ASIAN HOUSE-MARTIN Delichondasypus Rare winter visitor? Although
listed by Rashid (1967), the only confirmed record for Bangladesh is of a
flock of about 50-100 hawking for insects, with Barn Swallows and Red-
rumped Swallows (. Hirundo rustica and H. daurica ), over marshland, stubble
1004
Recent notable bird records from Bangladesh
35
fields and fires near Khagra, east of Sylhet (north-east) on 25 January 1993
(P.M.T.). Close views were obtained of several and identification was based
on the pale greyish underparts, dark underwing coverts, and scarcely forked
tail. The closest breeding areas for this species are in Nepal but it has also
been recorded from lowlands in north-east India (Inskipp and Inskipp 1991).
FLAVESCENT BULBUL Pycnonotus flavescens Vagrant or former local
resident. There is only one recent record: one seen in primary evergreen
forest at Kamarchera, Rajkandi (north-east) on 22 February 1985 (D.L.J.).
This forest has since been felled. As with a number of species from the hill
areas its status in the Chittagong Hilltracts is unknown because access is
restricted.
YELLOW-BELLIED PRINIA Prinia flaviventris Rare resident. Although
first recorded from the north-east by Godwin-Austen (1870), there have
been only five recent records. In the Sundarbans (south-west) one was
singing at Hiron Point on 29 January 1 984 (D.L.J.); about ten were in a small
marsh at Nilkamal on 10 February 1987 (D.A.S., S.M.A.R.); and six were
at the same site in March 1991 (D.A.S.). Elsewhere three were on a grassy
hillside in Nurjahan Tea Estate (Srimangal, north-east) on 25 June 1988
(D.J.M., P.M.T.); and two were singing between Chittagong and Rangamati
(south-east) on 22 April 1989 (D.L.J.).
CHESTNUT-HEADED TESIA Tesiacastaneocoronata Vagrant. Although
listed for the Chittagong Hilltracts in Ali and Ripley (1987), the only recent
record is of one in West Bhanugach Reserve Forest (north-east) on 24 March
1978 (D.L.J.).
**SLATY-BELLIED TESIA Tesia olivea Vagrant. The only record is of
one watched for 1 5 minutes at Madhapkhundo Waterfall (New Samanbagh
Tea Estate, north-east) on 24 December 1992 (D.L.J., J. & S.O’M.). Grey-
bellied Tesia Tesia cyaniventer is a relatively common winter visitor in the
area, but this bird was distinguished by the whole of the cap being bright
yellowish, and by a call which was similar but less harsh or sharp than that
of T. cyaniventer. T. olivea is listed for the nearby hillstates by Ali and Ripley
(1987), and may be a scarce altitudinal migrant to Bangladesh.
BROWNISH-FLANKED BUSH-WARBLER Cettia fortipes Rare winter
visitor? Although listed by Rashid (1967), and noted as breeding in the hills
of Meghalaya and wintering in the plains of north Bengal (Ali and Ripley
1987), there appears to be only one record. One was seen in Modhupur
Forest (central) in November 1986 (S.M.A.R.).
SPOTTED BUSH-WARBLER Bradypterus thoracicus Rare winter visitor?
First recorded from Sylhet (north-east) in the 1 9th century (Godwin-Austen,
1872). The only recent record is of one seen well in dense vegetation by
Pasua Beel, Gurmar Haor (north-east) on 24 April 1992 (D.A.S.).
LANCEOLATED WARBLER Locustella lanceolata Rare winter visitor?
36
P. M. THOMPSON et al.
Forktail 9
Although listed by Rashid (1967) and Ripley (1982), the only recent record
is of one seen well in herbaceous vegetation at Pasua Beel, Gurmar Haor
(north-east) on 4 March 1992 (D.A.S.).
GRASSHOPPER WARBLER Locustella naevia Rare winter visitor? Although
listed by Rashid (1967) and Ripley (1982), the only recent record is of one
seen well among crops by the Padma near Mawa south of Dhaka on 28
February 1986 (D.A.S.).
PALLAS’S WARBLER Locustella certhiola Possibly an uncommon passage
migrant, easily overlooked. Although listed for Bangladesh by Rashid
(1967), the only recent records are: one in a small marsh at Nilkamal,
Sundarbans (south-west) on 10 February 1987 (D.A.S., S.M.A.R.), one in
riverside scrub at Hail Haor (north-east) in April 1 987 (W.G.H.), at least five
in dense vegetation near Arabiakona Beel, Tangua Haor (north-east) on 23
April 1992 (D.A.S.), and two in a dense thicket at Pasua Beel (north-east)
on 24 April 1992 (D.A.S.).
* * B L A C K- B R O W E D REED-WARBLER Acrocephalus bistrigiceps Local
winter visitor and passage migrant, possibly overlooked previously. The first
record was of one in herbaceous vegetation with A. concinens l 'agricola for
comparison at Rauar Beel (Tangua Haor, north-east) on 3 March 1992
(D.A.S.). Subsequent records are of at least four singing in a large area of
rushes at Hail Haor (north-east) on 2 May 1992 (D.A.S.), and one in the
company of A. concinens I agricola in dense vegetation at Pasua Beel (north¬
east) on 26 January 1993 (P.M.T.). This species (which breeds in north-east
Asia) has been recorded as a winter visitor to West Bengal (regularly), eastern
Assam, and Manipur (Ali and Ripley 1987), so it is not unexpected in
Bangladesh.
PADDYFIELD WARBLER Acrocephalus a^nco/a/BLUNT-WINGED
WARBLER A. concinens Local winter visitor/passage migrant. A. agricola
has been collected in Bangladesh (Godwin-Austen 1870) and Ripley (1982)
listed A. concinens from Bangladesh. Harvey (1990) attributed all records of
these two species to A. agricola , but D.A.S. considered that, out of the
hundreds observed on passage through the wetlands of the north-east in late
April and early May 1992 (many of which were in song), those closely
observed were likely to be A. concinens. A. concinens stevensi breeds in Assam
and has been recorded in Bangladesh (Ali and Ripley 1987), but is difficult
to distinguish in the field from A. agricola ; further research is needed in
Bangladesh.
*SMOKY WARBLER Phylloscopusfuligiventer Vagrant?. The only confirmed
records of this species which winters in the Himalayan foothills are: one in
Modhupur Forest (central) on 26 November 1986 (C.S., S.M.A.R.), and
one in waterside scrub in the Botanical Gardens, Dhaka on 1 8 February 1 989
(W.G.H.).
1994
Recent notable bird records from Bangladesh
37
*RADDE’S WARBLER Phylloscopus schwarzi Vagrant/rare winter visitor.
The first record, and apparently the fifth for the Indian subcontinent - the
others being from Nepal (Inskipp and Inskipp 1991) and India (Jepson 1987)
- was of three feeding low down in a clump of bougainvillaea in Gulshan,
Dhaka on 15-20 December 1986 (W.G.H.). There are two subsequent
records: two in the Botanical Gardens, Dhaka on 20 December 1988
(W.G.H.); and one in mangrove forest at Tiger Point in the Sundarbans
(south-west) on 24 February 1992 (D.L.J.).
PALE-RUMPED WARBLER Phylloscopus chloronotus A rare winter visitor.
Although noted for Bangladesh in Ali and Ripley (1987), there are only two
recent records, both from the Botanical Gardens, Dhaka: one on 1 December
1988, and one on 18 February 1989 (both W.G.H.).
* YELLOWISH-BREASTED WARBLER (GREEN WARBLER)
Phylloscopus trochiloides nitidus A rare passage migrant, not specifically
mentioned for Bangladesh in Ali and Ripley (1987), although included in
Rashid (1967). The first confirmed record was of one closely watched at
Baroorah Tea Estate (Srimangal, north-east) in September 1986 (D.J.M.),
the only subsequent record is of one in the Botanical Gardens Dhaka on 26
October 1991 (D.L.J.). Although difficult to identify, in both cases the birds
were similar to but much brighter than accompanying Greenish Warblers P .
trochiloides trochiloides I vindanus, showing yellower underparts. This subspecies
has been recorded from Nepal in spring (Inskipp and Inskipp 1 99 1 ), and Ali
and Ripley (1987) regarded it as only a spring migrant through the Eastern
Himalayas.
^WESTERN CROWNED-WARBLER Phylloscopus occipitalis A regular
winter visitor, not noted for Bangladesh in Ali and Ripley (1987). The first
record was from West Bhanugach Reserve Forest (Srimangal, north-east) on
26 November 1985 (D.J.M.). Subsequently it has been frequently recorded
from October to March in forests and tea estates in the north-east and central
regions (W.G.H., D.L.J., D.J.M., C.S., P.M.T., J.D.W.).
* GREY-HOODED WARBLER Seicercus xanthoschistos Rare passage
migrant? Although listed by Rashid (1967) there are only three confirmed
records. The first record was from Shamshernagar Tea Estate (north-east)
in April 1986 (D.J.M.), subsequently single birds were seen in West
Bhanugach Reserve Forest, Srimangal (north-east) in March and April 1 987
(W.G.H., J.D.W.).
YELLOW-THROATED LAUGHINGTHRUSH Garrulax galbanus Rare
resident? Although listed by Ali and Ripley (1987) for the Chittagong
Hilltracts, the only recent record is of four bathing in a hill stream at Muchoni
near Teknaf (south-east) on 8 November 1983 (S.M.A.R.).
RUFOUS-VENTED LAUGHINGTHRUSH Garrulax gularis Rare
resident? Although listed from Bangladesh in Ali and Ripley ( 1 987), the onl>
38
P. M. THOMPSON et al.
Forktail 9
recent record is of one feeding on the ground by a stream in coastal scrub
jungle 5 km south of Cox’s Bazar (south-east) on 27 April 1988 (P.M.T.).
SPOT-THROATED BABBLER Pellomeum albiventre Rare resident.
Although listed for Bangladesh by Rashid (1967), there are few confirmed
records. In West Bhanugach Reserve Forest (Srimangal, north-east) one was
closely observed in November 1985 (D.J.M., E.F.G.), and two were seen in
June 1989 (W.G.H.).
MARSH BABBLER Pellomeum palustre Rare resident? Although recorded
from Sylhet in Hume (1888), and presumed to be a resident in marshy tree
jungle in Bangladesh (Ali and Ripley 1987) this threatened species (Collar
and Andrew 1988) has only been recorded once in recent years. Two were
seen in damp forest scrub in West Bhanugach Reserve Forest, Srimangal
(north-east) on 21 February 1989 (W.G.H.).
LARGE SCIMITAR-BABBLER Pomatorhinus hypoleucos Rare resident.
Although listed by Rashid (1967), there are only four recent records. One
in Satcheri Reserve Forest, Telepara (north-east) on 4 February 1982
(D.L.J.), one at Panerchara near Cox’s Bazar (south-east) in November
1983 (S.M.A.R.), two in dense bamboo in West Bhanugach Reserve Forest
(Srimangal, north-east) on 24 June 1 99 1 (P.M.T.), and two calling persistently
and attracted to tape playback at the same site on 1 5 May 1993 (N.B., R.H.,
D.L.J., J. & S.O’M., P.M.T.).
SPOT-BREASTED SCIMITAR-BABBLER Pomatorhinus erythrocnemis
Rare resident. Although listed for the Chittagong Hilltracts in Ali and Ripley
( 1 987), the only recent record is of one in coastal scrub jungle south of Cox’s
Bazar (south-east) on 28 April 1988 (P.M.T.).
* LONG-T AILED SIBIA Heterophasia picaoides Vagrant. The only confirmed
records are of at least four in a mixed species feeding flock in West Bhanugach
Reserve Forest (north-east) on 20 February 1989 (W.G.H.), and one in
Rajnagar Tea Estate between Moulvi Bazar and Kalaura (north-east) on 30
April 1992 (S.M.A.R.). These were presumably altitudinal migrants, as this
species is known from the nearby Indian hill states (Ali and Ripley 1987).
RUFOUS-HEADED PARROTBILL Paradoxomis ruficeps Vagrant? First
collected from south Sylhet by Primrose (1901), also a specimen from the
Rema Tea Estate, Luskarpore Valley near Habiganj (north-east) is held in the
collection of the Bombay Natural History Society (Abdulali 1 982). However,
the only recent records of this threatened species (Collar and Andrew 1 988)
are of a flock of at least five in dense bamboo in Nurjahan Tea Estate (north¬
east) on 23 February 1985, and again several in West Bhanugach Reserve
Forest (Srimangal) in an area adjacent to Nurjahan Tea Estate on 19 April
1985 (both D.J.M.); possibly the same birds were involved.
**LESSER WHITETHROAT Sylvia curruca Vagrant. The only record,
considered to show characters of the race S. c. blythi, is of one in song for two
1994
Recent notable bird records from Bangladesh
39
days in a tea estate at Srimangal (north-east) on 10 and 11 March 1990
(P.D.A., F.S., J.D.W.). This species is a common winter visitor to north¬
west India (Ali and Ripley 1987) and has even been recorded as far east as
Thailand (Boonsong and Round, 1991).
**ORPHEAN WARBLER Sylvia hortensis Vagrant. The only record is of
a male closely watched in coastal trees at Patenga (Chittagong, south-east)
on 7 December 1991 (P.M.T., D.L.J.). This species was previously known
to winter as far east as south Bihar (Ali and Ripley 1987) and the Kosi area
in eastern Nepal (Inskipp and Inskipp 1991).
THICK-BILLED FLOWERPECKER Dicaeum agile Rare resident?.
Although first recorded by Lister (1951), there are only five recent records.
One was associating with a mixed species feeding flock at Shilkhali near
Teknaf (south-east) on 20 August 1983 (S.M.A.R.). The remainder were all
seen in West Bhanugach Reserve Forest (Srimangal, north-east): one on 1 5
April 1987 (D.J.M.), one on 26 November 1987 (P.M.T.), one on 2
December 1988 (D.J.M.), and one in May 1989 (W.G.H.).
'‘'YELLOW-BELLIED FLOWERPECKER Dicaeum melanoxanthum
Vagrant. The only record is of a pair observed twice in West Bhanugach
Reserve Forest (Srimangal, north-east) on 23 February 1985 (D.L.J., N.B.).
These were presumably vagrants from higher altitudes in the Himalayas; Ali
and Ripley (1987) give a lowest altitude of 1400 m so this sighting at about
35 m is notable.
[OLIVE-BACKED SUNBIRD Nectarinia jugularis Vagrant? The record
from Sitapchar Reserve Forest, Kaptai (south-east), listed in Harvey (1990),
would have been the first for the Indian subcontinent outside of the Andaman
Islands, but is now regarded as only probable.]
GOULD’S SUNBIRD Aethopyga gouldiae Vagrant or rare passage migrant?.
First mentioned by Oates (1890), who noted that Hume recorded this
species from Chittagong, but that there were no specimens in his collection
from there. This is normally a species of higher altitudes than Bangladesh
and the only recent records are of a pair at Kuderm Cave, Harikhola (Teknaf,
south-east) on 6 March 1983 (S.M.A.R.), and a male closely observed in
West Bhanugach Reserve Forest (Srimangal, north-east) on 13 March 1985
(D.L.J.).
GREEN-TAILED SUNBIRD Aethopyga nipalensis Status uncertain.
Although listed for the Chittagong Hilltracts and at altitudes down to 300 m
in Ali and Ripley (1987), the only recent record is of a male in West
Bhanugach Reserve Forest (Srimangal, north-east) on 22 February 1990
(P.D.A., F.S.).
EURASIAN TREE SPARROW Passer montanus Rare resident. The only
recent record is of a pair watched copulating on a garden wall in the western
suburbs of Sylhet (north-east) on 20 April 1992 (D.A.S.). Although Harvey
40
P. M. THOMPSON et al.
Forktail 9
(1990) gives the only past locality in Bangladesh as the Chittagong Hilltracts,
P. m. malaccensis is a common resident in Assam and Meghalaya (Cachar,
Khasi and Garo Hills) (Ali and Ripley 1987), and can be expected in the
adjoining north-east of Bangladesh.
BLYTH’S PIPIT Anthus godlewskii A rare passage migrant?. Although listed
for Bangladesh by Rashid (1967), the only definite records of this species,
which may have been overlooked in the past, are: at least 12 in Dhaka Zoo
on 23 April 1988 (W.G.H., P.M.T.); 20+ by the river at Srimangal (north¬
east) on 14 May 1988; four at Dhaka Zoo on 29 October 1988; and at least
two on the Ganges sandflats at Rajshahi (north-west) in February 1989 (all
W.G.H.).
**RED-THROATED PIPIT Anthus cervinus Probably a scarce winter
visitor to wetlands in the north-east. Although Rashid (1967) assumed that
it would occur, the first records for Bangladesh are of at least eight individuals
recorded during wetland surveys in the north-east in February-March 1 992.
Two were near Hakaluki Haor on 1 9 February, four were in wet paddy fields
near Puala Beel (Hakaluki Haor) on 20 February, and at Kawadighi Haor
there was one on 22 February and two on 8 March (all D.A.S., latter also
S.M.A.R.). It seems likely that this species has been overlooked in the past.
Although this species is regular in winter in Pakistan and on passage in Nepal,
there are few records from elsewhere in the Indian subcontinent. The closest
records are from Manipur and the Andaman and Nicobar Islands (Ali and
Ripley 1987).
COMMON ROSEFINCH Carpodacus erythrinus Rare winter visitor.
Although first recorded from Dhaka area by Tytler (1854), there are only
three recent records. A male was at Sitakunda Hills, Chittagong (south-east)
on 12 December 1987 (N.B., R.H.); 3-4 were feeding in scrub at Katka in
the Sundarbans (south-west) on 16 December 1988 (W.G.H.); and a male
was in the Port Authority compound at Nilkamal (Sundarbans, south-west)
on 24 March 1991 (D.A.S., S.M.A.R.).
CHESTNUT-EARED BUNTING Emberiza fucata Locally common
winter visitor. Although listed by Ali and Ripley ( 1 987) as a winter visitor to
most of Bangladesh, Harvey (1990) gave no recent records. The first recent
record is of two in crops by the Padma near Mawa, south of Dhaka, on 28
February 1986 (D.A.S.). Subsequently D.A.S. and S.M.A.R., in surveys of
wetlands in the north-east, found this species to be fairly common between
5 March and 2 May 1 992 with a total of 3 1 bird days from seven sites: Dubrair
Haor (maximum count of at least 20 on 5 March 1 992), Meda Beel, Dekhar
Haor, Arabiakona Beel, Maijeil Haor, Chatla Beel (Hakaluki Haor), and
Hail Haor. Four were found at Medkol Beel, Bara Haor (also north-east) on
29 January 1993 (S.M.A.R.). This is a rather secretive species which would
appear to have been overlooked in Bangladesh in the past.
1994
Recent notable bird records from Bangladesh
41
LITTLE BUNTING Ernberiza pusilla Rare winter visitor. First recorded
from Sylhet by Hume (1888), Ali and Ripley (1987) list it as a migrant to the
Chittagong Hilltracts, but there are only three recent records. Two flocks
totalling about 10 birds were on a hillside freshly prepared for planting tea
near Snmangal (north-east) on 14 February 1986 (P.M.T.); one was by a
track leading to Hail Haor (Srimangal) on 9 December 1988 (D.J.M.,
J.D.W.); and one was in a plantation at Bogi on the eastern edge of the
Sundarbans (south-west) on 18 March 1991 (D.A.S.).
DISCUSSION
The above 147 species fall into three categories. Long distance migrants
which occur as vagrants or which are regular visitors, and which were
overlooked in the past (waders such as Spotted Redshank and some migrant
warblers and buntings) . Altitudinal or local migrants which breed within the
sub-continent and which may be regular in small numbers or are vagrants
from the Himalayas and adjacent hill states. Finally, species which may be
rare residents since they do not make regular movements (Table 1). Recent
fieldwork has been concentrated in the wetlands and forest areas. A number
of the species recorded from ‘other’ habitats (Table 1) make use of either
wetlands or forest, but are also found in open country or homestead
woodland. During the 1980s attention focused on the coastal mudflats,
while in 1992-1993 regular surveys of the major wetlands in the north-east
have revealed much new information.
It is remarkable that of the 147 species discussed in this paper no less than
60 have been recorded from a small area around Srimangal town in the north¬
east; an area comprising the wetlands of Hail Haor, tea estates, and West
Table 1 Habitat, origin and status of recent notable birds in Bangladesh.
42
P. M. THOMPSON et al.
Forktail 9
Bhanugach Reserve Forest. Moreover 36 of the species discussed in this
paper have been recorded in West Bhanugach Reserve Forest (including 1 5
which are new for Bangladesh since 1978). This small area must be regarded
as the best and most accessible area of evergreen forest (a mixture of natural
forest and old teak plantations) remaining in Bangladesh, but it is under
constant human pressure for bamboo and timber. Unfortunately several
other forests, and parts of West Bhanugach Reserve Forest, have been clear
felled in recent years, they have at best been replanted with monocultures of
quick growing trees which are of negligible ornithological interest.
There are about 1 00 species for which there are still no recent records, but
which are listed by Harvey (1990) as occurring in Bangladesh on the basis of
historical records, mostly from the Chittagong Hilltracts. There have also
been 59 new species for Bangladesh since 1978. Hence there is still much
scope for new discoveries in this ornithologically diverse but understudied
country, so long as the remaining small patches of relatively natural forests
and wetlands can be preserved.
We are grateful to Tim Inskipp for providing details of his extensive review of historical references; and
especially to all those observers who provided details of their records.
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Oxford University Press.
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Collar, N. J. and Andrew, P. (1988) Birds to watch. The ICBP world check-list of threatened birds.
Cambridge, U.K.: International Council for Bird Preservation.
Collins, S. J. K. (1948) Birds of the Lalmai area, near Comilla, Tippera, Bengal (observed between
December 1944 and end of July, 1945). J. Bombay Nat. Hist. Soc. 47: 57-69.
Cripps, J. R. (1878) First list of the birds of Fureedpore, eastern Bengal. Stray Feathers 7:238-315.
Evans, M. (1881) [Wildfowl in Sylhet]. Stray Feathers 10: 163-165.
Gardiner, S. (1991) Mandarin Duck Aix galericulata: a new species for Nepal. Forktail 6: 87-88.
Godwin-Austen, H. (1870) Second list of birds obtained in the Khasi and North Cachar hill ranges
including the Garo Hills and country at their base in the Mymensingh and Sylhet districts. J. Asiatic
Soc. Bengal 39(2): 264-275.
Godwin-Austen, H. (1872) Third list of birds obtained in the Khasi and Garo hills ranges, with some
corrections and additions to the former lists. J. Asiatic Soc. Bengal 41(2): 142-143.
Harvey, W. G. (1990) Birds in Bangladesh. Dhaka: University Press Ltd.
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Hume, A. O. (1888) The birds of Manipur, Assam, Sylhet and Cachar. Stray Feathers 1 1 : 1-353.
Husain, K. Z. (1968) Field-notes on the birds of the Chittagong Hill-Tracts. (Notes based on the records
of the Asiatic Society of Pakistan Expedition to the Chittagong Hill-Tracts, 1965), Paper V: Non¬
passerine birds. J. Asiatic Sac. Pakistan 13: 91-101.
Husain, K. Z. (1979) Birds of Bangladesh. Dhaka: Government of Bangladesh.
Husain, K. Z. and Haque, M. N. (1976) Further additions to the list of birds of Pablakhali Wildlife
Sanctuary (the Chittagong Hill-Tracts). Bangladesh J. Zool. 4: 131-132.
Husain, K. Z., Sarker, S. U., and Khan, A. R. (1974) Birds of Dacca with some notes on their present
status). Bangladesh J. Zool. 2: 153-170.
Husain, K. Z., Sarker, S. U., and Rahman, M. (1983) Summer birds of the Sundarbans’ ‘Nilkamal
Sanctuary’, Bangladesh. Bangladesh J. Zool. 11:48-51.
Inskipp, C. and Inskipp, T. P. (1991) A guide to the birds of Nepal. Second edition. London: Christopher
Helm.
Jepson, P. (1987) Recent reports. Oriental Bird Club Bull. 6: 36-40.
Katti, M. (1992) Biodiversity and the exploitation of wild fruits in the tropical forests of Arunachal
Pradesh, India. Unpublished project summary.
Khan, M. A. R. (1982) Wildlife of Bangladesh: a checklist. Dhaka: University of Dhaka.
Khan, M. A. R. (1985) St Martins - a vanishing coral island of Bangladesh. Tigerpaper 12(4): 6-12.
King, B., Dickinson, E. C. and Woodcock, M. W. (1975) A field guide to the birds of South-East Asia.
London: Collins.
Koelz, W. (1954) Ornithological studies. I. New birds from Iran, Afghanistan and India. Contrib. Inst.
Regional Exploration 1: 1-32.
Lister, M. D. (1951) Some bird associations of Bengal. J. Bombay Nat. Hist. Soc. 49:695-728.
Meyer de Schauensee, R. (1984) The birds of China. Oxford: Oxford University Press.
Mountfort, G. and Poore, D. ( 1 968) Report on the second World Wildlife Fund Expedition to Pakistan.
(WWF Project 311). Unpublished report. Gland, Switzerland: WWF.
Oates, E. W. (1890) Fauna of British India. Birds, 2. London: Taylor and Francis.
Prater, S. H. (1926) The occurrence of the Giant Heron ( Ardea goliath) in the Khulna District, Bengal.
J. Bombay Nat. Hist. Soc. 31: 523.
Primrose, A. M. (1901) Notes on birds collected in south Sylhet. J. Bombay Nat. Hist. Soc. 13: 707-
708.
Rashid, H. (1967) Systematic list of the birds of East Pakistan. Publication no. 20. Dacca: The Asiatic
Society of Pakistan.
Rashid, S. M. A. and Khan, A. Z. (1987) Waterfowl of the Teknaf Peninsula, Bangladesh. Paper
presented at the Conference on Wetlands and Waterfowl Conservation in Asia, Malacca, Malaysia,
23-28 February 1987. IWRB and Interwader.
Ripley, S. D. (1982) A synopsis of the birds of India and Pakistan together with those of Nepal, Bhutan,
Bangladesh and Sri Lanka. Bombay: Bombay Natural History Society.
Savage, C. D. W. (1970) S.W. Asia survey. International Wildfowl Research Bureau Bulletin 30: 1 1-14.
Scott, D. A. and Rose, P. M. (1989) Asian waterfowl census 1989. Slimbridge, UK: International
Waterfowl and Wetlands Research Bureau.
Simson, F. B. (1882) Notes on birds found near Dacca. Ibis 4(6): 84-95.
Smythies, B. E. (1986) Birds of Burma. Third edition. London: Nimrod Press.
Stanford, J. K. (1937) On the breeding of the Oystercatcher ( Haematopus ostralegus subsp.) and other
birds in the Bengal Sunderbunds. J. Bombay Nat. Hist. Soc. 39: 867-968.
Stanford, J. K. (1954) A bewilderment of birds. London: Hart-Davis.
Tvtler, R. C. (1854) Miscellaneous notes on the fauna of Dacca, including remarks made on the line
of march from Barrackpore to that station. Ann. Mag. Nat. Hist. 2(14): 168-177.
van der Ven, J. (1988) Asian waterfowl - 1988. Slimbridge, U.K.: International Waterfowl Research
Bureau.
Weston, W. V. (1914) Small game shooting in Sylhet. J. Bombay Nat. Hist. Soc. 23: 367-368.
44
P. M. THOMPSON et al.
Forktail 9
Paul M. Thompson, Middlesex University, Queensway, Enfield, EN3 4SF, U.K.
W. G. Haruey, The British Council, PO Box 40751, Nairobi, Kenya.
David L. Johnson, House 52, Road 11, Banani, Dhaka, Bangladesh
David J. Millin, Furzemoor Cottage, Cold Harbour, Goring Heath, Reading, RG8 7SY, U.K.
S. M. A. Rashid, Nature Conservation Movement (NACOM) , House 16, Road 2, Banani, Dhaka,
Bangladesh.
D. A. Scott, Runagate, Far Green, Coaley, Dursley, Gloucestershire, GL11 5EL, U.K.
Craig Stanford, Department of Anthropology, University of Southern California, Los Angeles, CA 90089-0032,
U.S.A.
John D. Woolner, 1 Priory Close, Harrold, Bedfordshire, MK43 7DL, U.K.
APPENDIX 1
LIST OF INITIALS AND CONTRIBUTORS OF NOTABLE
RECORDS
R.A.
A.W.A.
P.D.A.
D. B.
M. A.B.
N. B.
G.F.
E. F.G.
J.H.
R.H
Raguibuddin Ahmed
A. Wahab Akonda
Peyo D’Andurian
David Bakewell
Mark A. Barter
Nalini Bayen
Graham Frazer
E.F. Grimes
John Howes
Ronnie Haider
W.G. Harvey
David L. Johnson
Altamash Kabir
Anisuzzaman Khan
W.G.H.
D.L.J.
A.M.K.
A.K.
R. K.
H. & C.L.
D.J.M.
J. & S.O’M
S. M.A.R.
F.S.
D.A.S.
M.S.
C.S.
P.M.T.
A.W.
P.L.W.
J.D.W.
V.Z.
Reza Khan
HansHans and Christina Lamosse
David J. Millin
.John and Sue O’Malley
S.M.A. Rashid
Francois Sargot
Derek A. Scott
Murray Smith
Craig Stanford
Paul M. Thompson
Ann Wheeler
P.L. White
John D. Woolner
N.P. van Zalinge
1994
FORKTAIL 9 (1993): 45 - 57
45
Birds recorded in the Great Himalayan
National Park, Himachal Pradesh,
India
ANTHONY J. GASTON, PETER J. GARSON and SANJEEVA
PANDEY
Recent information on the avifauna of the Great Himalayan National Park in the Kullu District of
Himachal Pradesh, India is provided. Most observations were obtained from the Himachal Wildlife
Project, a series of forest wildlife surveys conducted mainly in spring and autumn during 1980-91 . So
far, 183 species of birds, including 132 passerines, have been recorded in the Park and on its western
approaches. These data provide evidence of sympatric populations of Dark-grey Tit Pants nt/onuchalis
and Rufous-vented Tit P. nibidiventris, and a substantial range extension for Little Pied Flycatcher
Ficedula westermanni. Two sightings of White-browed Shortwing Brachypteryx montana are thought to
be the first in the western Himalaya.
A great deal of information has been accumulated in the past two decades on
the birds of the Nepal Himalaya, about which little was known prior to the
1970s (Inskipp 1989, Inskipp and Inskipp 1991). By contrast the Indian
Himalaya, so well visited during the British period, has received much less
attention since Indian independence. Kashmir and Ladakh have remained
popular destinations for ornithologists (e.g. Williams and Delaney 1986,
Holmes 1 986, Mallon 1987), but there has been very little published on birds
in Himachal Pradesh, which represents the heart of the western Himalaya
(Schaller 1 977). In this paper we describe recent observations on birds in the
Great Himalayan National Park, Himachal Pradesh, which lies in this region
and contains a complete suite of the temperate and subalpine forest types
characteristic of front ranges in this part of India.
The Great Himalayan National Park is situated in Seraj Tehsil of Kullu
District, Himachal Pradesh. It was created in 1984, following
recommendations provided by the Himachal Wildlife Project, a joint U.K.,
U.S.A. and Indian project to assess the status of wildlife and wildlife habitats
in Himachal Pradesh (Gaston et al. 1981, 1983). The Park covers 620 km2,
over an altitude range of 1,700-5,800 m (Singh et al. 1990), and comprises
the headwaters of three left bank tributaries of the River Beas: the Jiwa, Sainj,
and Tirthan (Figure 1).
The climate of the Park is typical of the front ranges of the western
Himalaya. Precipitation is moderate over most of the year and abundant
during the monsoon season in June-August. In winter snow falls throughout
the park, although it generally does not lie long at the lowest altitudes. Above
3,000 m snow generally persists from November to March.
46
A. J. GASTON, P. J. GARSON and SANJEEVA PANDEY
Forktail 9
Figure 1 . Location of the Great Himalayan National Park (stippled area) within the upper Beas Valley,
near Kullu in central Himachal Pradesh. The inset shows Himachal Pradesh (HP) on an outline of India.
About one third of the area of the Park supports closed canopy forest,
which extends from the valley bottoms to 3,300-3,600 m, depending on
aspect. A little over half of the area lies above 4,000 m, which is approximately
the upper boundary of the subalpine and alpine scrub communities in this
part of the Himalaya (Champion and Seth 1968, Gaston ct al. 1981). The
forested areas support good examples of most vegetation types representative
of the area, including extensive stands of Kharsu Oak Quercus semecarpifolia,
Horse Chestnut Aesculus indica , Birch Betula alnoides , Himalayan Blue Pine
1994
Birds recorded in the Great Himalayan National Park
47
(Kail) Pinus wallichiana, West Himalayan Silver Fir Abies pindrow, West
Himalayan Spruce Picea smithiana and Himalayan Cedar Cedms deodara , as
well as smaller areas of the lower altitude oaks, Ban Q. leucotnchophora and
Moru Q. floribunda. Himalayan Yew Taxus baccata ssp. wallichiana is an
important understory tree in places. Pure stands of any species are relatively
rare, most of the forest being mixed to some degree.
Several clearings (‘thach’) used for grazing occur within the forest zone.
The forest surrounding such clearings tends to have an open understorey and
the vegetation shows signs of damage by grazing. The Himalayan Balsam
Impatiens glandulifera is common in such areas, forming extensive patches of
ground cover. Elsewhere, especially where slopes are very steep, the forest
has a dense understorey of Ringal Bamboo Thamnocalamus spathiflora and
shrubs.
The subalpine zone is dominated by a low forest of Himalayan Birch B.
utilis, Cherry Prunus comma and fir, or by dense stands of Rhododendron
campanulatum up to about 3 m high. Common Juniper Juniperus communis
scrub occurs in the lower part of the alpine zone, above about 3,700 m.
Higher up, the vegetation consists principally of herb communities which are
very diverse and luxuriant in places.
The area of the Great Himalayan National Park was judged by members
of Himachal Wildlife Project to support the best examples of undisturbed
West Himalayan temperate forest that they encountered during extensive
surveys throughout most of Himachal Pradesh in 1978-1980. Consequently
it should support a near-complete sample of both resident and migrant
species regarded as characteristic of the West Himalaya. The Park also falls
within one of the globally important Endemic Bird Areas (D02: Western
Himalayas) identified by the ICBP Biodiversity Project (ICBP 1992).
Previously the birds of the Kullu Valley have been listed by Whistler ( 1926a),
who also produced a more extensive list of birds for the adjacent Kangra
Valley (Whistler 1 926b) . He visited the Seraj Tehsil, but his list specified only
a few species from there and it is unlikely that he penetrated the Park area,
which is not on any regularly-used track and does not contain any rest-house.
Both Whistler (1926a) and Babault (1920) visited Pulga, in the Parbati
Valley, only a day’s walk from the Park boundary (Figure 1), while Wynter-
Blyth (1952) passed through the Tirthan Valley not far from the Park. There
is no published account reporting birds from the actual Park area.
The ornithology of the Great Himalayan National Park area has been
investigated since 1980 by a number of parties affiliated to the Himachal
Wildlife Project. Visits were made during 22-26 March, 14-18 April, 22-26
May, 7-16 September and 9- 1 2 October in 1980; 13-18 March, 30 March-
8 April, and 29 April-3 May in 1983; 13-15 November in 1985; 5-14and21-
29 September, and 9-16 and 26-30 October in 1991 (Gaston and Garson
1992). Other observations have also been contributed by the staff of the
48
A. J. GASTON, P. J. GARSON and SANJEEVA PANDEY
Forktail 9
National Park and by B. King (pers. comm.)? who visited the area from 27
September to 2 October 1984. This paper summarises all records of birds
within the Park up to November 1991.
Because there is no road access to the Park all visitors need to walk in along
one of the several trails that give access to it. We have included in our list all
species seen within the Park boundaries and also those recorded between the
roadheads at Ropa or Sainj (in the Sainj Valley), or Gushaini (in the Tirthan
Valley) and the Park boundary (Figure 1).
Plant names follow Polunin and Stainton ( 1 984) . For birds, nomenclature
follows Sibley and Monroe (1990).
RESULTS
Himachal Wildlife Project survey parties and the National Park staff have
recorded 168 species of birds in the Great Himalayan National Park and a
further 1 1 species on the approach paths. Another four species were reported
by B. King, making 183 species in total to date (Table 1). The list comprises
5 1 non-passerines and 1 32 passerines. This compares with 7 1 non-passerines
and 1 50 passerines recorded by Himachal Wildlife Project parties throughout
the hilly regions of Himachal Pradesh above 1,500 m altitude in 1980
(Gaston etal. 1981), suggesting that the Park supports a substantial proportion
of all the species occurring within its altitudinal range in the western
Himalayas.
At least 50 species are summer visitors to the Park(e.g. Eurasian Woodcock
Scolopax rusticola, cuckoos Cuculus, Oriental Turtle-Dove Streptopelia orientalis,
swifts, Grey Nightjar Caprirnulgus indicus, drongos Dicrums, swallows, most
flycatchers and warblers, many chats and thrushes). Other resident species
may move to lower altitudes within the Beas catchment for the harshest mid¬
winter period, during which we have done little work. Thus we have also only
recorded three winter visitors so far, and more may well occur only then. No
species could be described definitely as passage migrants, although Short¬
eared OwMszo flammeus, Fork-tailed SwiftHpws pacificus, Eurasian Chiffchaff
Phylloscopus sindianus and Tickell’s Leaf-Warbler P. affinis may fall into that
category.
Raptors
Both Himalayan Griffon Gyps himalayensis and Lammergeier Gypaetus
barbatus were common in the Park, being seen daily at all seasons. Golden
Eagle Aquila chrysaetos and Common Buzzard Buteo buteo were seen frequently
at all seasons in the subalpine and alpine zones. Eurasian Sparrowhawk
Accipiter nisus was common below the tree line. Black Eagle Ictinaetus
1994
Birds recorded in the Great Himalayan National Park
49
malayensis and Booted Eagle Hieraaetus pennatus were recorded only twice
each. There was no record of Peregrine Falcon Falco peregrinus from the Park.
This species appears to have become very rare in the western Himalaya.
Gamebirds
The Great Himalayan National Park is one of only two National Parks in the
world to support a population of the threatened Western Tragopan Tragopan
melanocephalus (Collar and Andrew 1988), the other being Machiara National
Park in Pakistan (G. Duke, pers. comm.). Males were heard calling during
both spring surveys (1980, 1983), and in October 1991 two family parties
were encountered, and birds were also seen in the Tirthan Valley just outside
the Park boundary. The altitudinal range of these records was 2,100-3,100
m.
The Impeyan Monal Lophophorus impejanus and Koklass Pheasant Pucrasia
macrolopha were abundant in the temperate forest zone, and Monal also
occurred in subalpine scrub, especially in autumn. Kalij Pheasants Lophura
leucomelanos occurred in small numbers below 2,000 m, while some steep
south-facing slopes covered by grasses and shrubs supported small numbers
of the Cheer Pheasant Catreus wallichii (Garson et al. 1992). The Hill
Partridge Arborophila torqueola occurred sparingly at altitudes below 2,500
m. The Snow Partridge Lerzua lerzua has been recorded just once in the Park,
above the tree-line in the Tirthan Valley during November 1 99 1 (M. Bhaik,
pers. comm.) . The only other sighting reported by Himachal Wildlife Project
parties was of a covey in the Jagatsukh Valley, which lies about 50 km north¬
west of the Park near Manali (Figure 1), in October 1985 (A.J.G., pers. obs.).
This species is clearly rather rare in the front ranges of the western Himalaya.
Shorebirds
Eurasian Woodcock were recorded roding at several localities within the Park
and in adjacent forested areas between 1,900-3,000 m. It is presumably a
regular breeder. The Solitary Snipe Gallinago solitaria was recorded in
autumn 1991 on two small marshes at about 4,000 m elevation.
Pigeons
The Speckled Wood-Pigeon Columba hodgsonii and Snow Pigeon C. leuconota
were both common in the Park, as was the Oriental Turtle-Dove in summer.
Parakeets
The Slaty-headed Parakeet Psittacula himalayana, seen commonly in forest
up to 2,200 m, was the only species recorded.
50
A. J. GASTON, P. J. GARSON and SANJEEVA PANDEY
Forktail 9
Cuckoos
All species were summer visitors to the forests, the Common Cuckoo Cuculus
canorus and the Oriental Cuckoo C. saturatus being encountered most
frequently.
Owls
The Collared Owlet Glaucidium brodiei and the Tawny Owl Strix aluco were
both common in the temperate forest zone and the Mountain Scops-Owl
Otus spilocephalus was recorded on several dates. The Rock Eagle-Owl Bubo
bengalensis and Short-eared Owl were recorded only once.
Other non-passerines
The Grey Nightjar was common during April-September up to 3,000 m.
Himalayan Swiftlets Collocalia brevirostris and Fork-tailed Swifts Apus pacificus
were recorded frequently from April to October, occurring mainly over
forests. There was one record for the White-throated Needletail Hirundapus
caudacutus. The Eurasian Hoopoe Upupa epops occurred up to 2,500 m
during April-September. Brown-fronted Woodpecker Dendrocopos auriceps
and Great Barbet Megalaima virens were both recorded up to 2,000 m, while
the Scaly-bellied Woodpecker Picus squamatus and Himalayan Woodpecker
Dendrocopos himalayensis occurred throughout the temperate forests. The
Speckled Piculet Picumnus innominatus was present only at the lowest
altitudes (below 2,000 m).
Passerines
Like most Himalayan forests, those of the Great Himalayan National Park
are rich in babblers (Garrulacinae and Sylviinae: Timaliini, 14 species),
flycatchers (Muscicapinae: Muscicapini, 1 1 species), chats (Muscicapinae:
Saxicolini, 1 1 species), warblers (Acrocephalinae, 14 species), and Thrushes
(Turdinae, 12 species), which together comprised just under 50% of
passerines recorded. Our records of three particular species appear to be
noteworthy:
White-browed Shortwing Brachypteryxmontana. One female was seen in
the Jiwa Valley in September 1991 (S. Westerberg, pers. comm.) and one of
unknown sex was seen by A J.G. in the Tirthan Valley on the approach to the
Park in October 1991 . Although Ali and Ripley (1983) give the range of this
bird as extending west to Tehri Garhwal, there does not appear to be any
authentic previous record west of Nepal. The reference cited by Ali and
Ripley for Garhwal (Osmaston 1 897) does not mention the species, and the
inclusion of Shimla (Himachal Pradesh) and Garhwal by Baker ( 1 924) is not
1094
Birds recorded in the Great Himalayan National Park
51
supported by specific references. Thus our records appear to be the first for
the western Himalaya and extend the known range of this species by some
400 km to the north-west.
Little Pied Flycatcher Ficedula westermanni. Two males were seen in
the Sainj Valley (one singing) and one female was trapped and photographed
at Majhan in the Jiwa Valley, all in September 1991 (S. Westerberg and A.
Starling, pers. comm.). This species is said by Ali and Ripley (1983) not to
occur west of Nepal, but it is reported by Green (1986) from Kedarnath
Wildlife Sanctuary in Garhwal (Uttar Pradesh) . Our records extend its range
by a further 200 km to the north-west.
Rufous-vented T it Pams mbidiventris . Single individuals were seen twice
in mixed feeding parties with Black-crested Tits P. melanolophus and warblers
in coniferous forest above 3,000 m in the Tirthan Valley in October 1991
(A.J.G., pers. obs.). This species was also recorded by A.J.G. in subalpine
scrub in the Jagatsukh Valley (Figure 1) in October 1985. Ali and Ripley
(1983) regarded this bird as conspecific with the Dark-grey Tit P. mfonuchalis ,
and gave its western range limit as Tehri Garhwal. However, Green (1986)
recorded this species as occurring in Kedarnath Wildlife Sanctuary, and
Jones (1944) reported it from Chor Dhar, just east of Shimla. The Rufous-
vented and Dark-grey Tits have previously been reported as occurring
sympatrically in central Nepal and at Overa Wildlife Sanctuary in Kashmir
(Jamdar and Price 1990). Like us in autumn, these authors only found the
Rufous-vented Tit close to the tree-line in spring, and observed the Dark-
grey Tit to have a much broader and generally lower altitudinal distribution.
CONCLUSIONS
The Great Himalayan National Park provides excellent opportunities for
viewing the avifauna of the Western Himalayan front ranges. With the
progressive destruction of much of the mature forest elsewhere in Kullu
District, the large block of virtually undisturbed habitats provided by the
Park should assure the persistence of species such as Northern Goshawk
Accipiter gentilis, Black Eagle, Booted Eagle, Western Tragopan, Tawny Owl,
and Long-billed Thrush Zoothera monticola, which probably require substantial
areas of natural forest for their survival.
Ornithological investigations of the Park are by no means complete. In
particular, the alpine areas have been little visited in summer, so the list of
high altitude breeders is almost certainly incomplete. In addition there have
been few observations between November and February, when high altitude
species may be driven down into the valley bottoms by heavy snow.
Observations in winter, even at low altitudes, would also help to clarify the
migratory status of many species. Further work in spring and summer is
52
A. J. GASTON, P. J. GARSON and SANJEEVA PANDEY
Forktail 9
required to establish whether or not most of the species recorded so far
actually breed within the Park, and if so, over what sort of altitude range and
in which particular forest types. Visits in May, when weather conditions are
usually good, would be especially valuable for this purpose.
Anyone wishing to carry out ornithological studies in the western Himalayas
will find the Great Himalayan National Park an excellent area in which to
work. A good network of trails is maintained in all three main valleys by the
Park staff. In 1991 they also constructed or refurbished several huts, which
can accommodate visitors. Arranging access to facilities, as well as guides and
porters, should be done by contacting the Director, Great Himalayan
National Park, Department of Forest Farming and Conservation, Shamshi,
Kullu District, Himachal Pradesh. The authors would be most interested to
receive notes on any bird observations made in Kullu District and especially
within the National Park.
We would like to thank all those members of the Wildlife Wing of the
Himachal Pradesh Department of Forest Farming and Conservation (DFFC),
who did so much to make our various survey trips both productive and
enjoyable. For assistance in 1991 we would like to thank especially the Chief
Wildlife Warden, B. S. Chauhan, the outgoing Director of the Park, Vijay
Kumar, and the new Director, Manoj Bhaik, for their enthusiastic support,
and M. P. Sharma and B. R. Negi for their their help and companionship in
the field.
For financial support in 1991 we are grateful to the International Trust for
Nature Conservation, the Oriental Bird Club and World Wide Fund for
Nature-India. We would like to thank Aligarh Muslim University and the
Canadian Wildlife Service for the loan of equipment.
We also thank all those outside the Wildlife Wing who worked with us in
the field in 1991: Dr H. S. A. Yahya, Afif U. Khan, Ashfaque Ahmed and
Rashid H. Raza (Centre of Wildlife and Ornithology, Aligarh Muslim
University), Virinder Sharma (H. P. Council for Science, Technology and
Environment), Ajay Rastogi (WWF-India), Vishal Bhopal (Kullu Naturalists
Club), Anne and Stephen Westerberg and Anne-Marie Gaston. Many
thanks are also due to Mr Vindri Singh and his family from Shangarh for
hospitality and medical assistance, and to Mr Ranjiv Bharti and family for
advice and entertainment. Finally we thank Ben King for the use of his
unpublished records.
1994
Birds recorded in die Great Himalayan National Park
53
REFERENCES
Ali, S. and Ripley, S. D. (1983) Handbook of the birds of India and Pakistan. Compact Edition. New Delhi:
Oxford University Press.
Babault, G. (1920) Mission Guy Babault dans les provinces centrales de I’Inde, dans la region occidentale de
l' Himalaya et Ceylan, 1914. Resultats scientifiques, oiseaux. Paris: Musee National d’Histoire Naturelle.
Baker, E. C. S. (1924) The fauna of British India, including Ceylon and Burma. Birds, 2. Second edition.
London: Taylor and Francis.
Champion, H. G. and Seth, S. K. (1968) A revised survey of the forest types of India. New Delhi:
Government of India.
Collar, N. J. and Andrew, P. (1988) Birds to watch: the ICBP world checklist of threatened birds. Cambridge,
U.K.: International Council for Bird Preservation (Techn. Publ. 8).
Garson, P. J., Young, L. and Kaul, R. (1992) Ecology and conservation of the Cheer Pheasant Catreus
wallichii : studies in the wild and the progress of a reintroduction project. Biol. Conserv. 59: 25-35.
Gaston, A. J. and Garson, P. J. (1992) Himachal Wildlife Project - III. A re-appraisal of the Great Himalayan
National Park. Unpublished.
Gaston, A. J., Hunter, M. L. and Garson, P. J. (1981) The wildlife of Himachal Pradesh, Western
Himalayas. University of Maine School of Forest Resources Technical Report No. 82.
Gaston, A. J., Garson, P. J. and Hunter, M. L. (1983) The status and conservation of forest wildlife in
Himachal Pradesh, Western Himalayas. Biol. Conserv. 27: 291-314.
Green, M. J. B. (1986) The birds of Kedarnath Sanctuary, Chamoli District, Uttar Pradesh: status and
distribution. J. Bombay Nat. Hist. Soc. 83: 603-617.
Holmes, P. R. (1986) The avifauna of the Suru River Valley, Ladakh. Forktail 2: 21-41.
I.C.B.P. (1992) Putting biodiversity on the map: priority areas for global conservation. Cambridge, U.K. :
International Council for Bird Preservation.
Inskipp, C. (1989) Nepal’s forest birds: their status and conservation. Cambridge, U.K.: International
Council for Bird Preservation. (Monograph 4).
Jamdar, N. and Price, T. ( 1 990) Simla BlackTit Pants rufonuchalis and Rufous-bellied Crested Tit Pants
ntbidiventris breeding sympatrically in Kashmir. J. Bombay Nat. Hist. Soc. 87: 302-303.
Jones, A. E. (1944) On the occurrence of the Rufous-bellied Crested Tit ( Lophophanes ntbidiventris ) in
the Simla Hills. J. Bombay Nat. Hist. Soc. 44: 474-475.
Jones, A. E. (1944) On the occurrence of the Rufous-bellied Crested Tit ( Lophophanes ntbidiventris ) in
the Simla Hills. J. Bombay Nat. Hist. Soc. 44: 474-475.
Osmaston, B. B. (1897) Birds nesting in the Tons Valley. J. Bombay Nat. Hist. Soc. 1 1 : 468-473.
Mallon, D.P. (1987) The winter birds of Ladakh. Forktail 3: 27-41.
Polunin, O. and Stainton, A. (1984) Flowers of the Himalayas. New Delhi: Oxford University Press.
Schaller, G. B. (1977) Mountain monarchs. Chicago: Chicago University Press.
Sibley, C. G. and Monroe, B. L., Jr. (1990) Distribution and taxonomy of birds of the world. New Haven
and London: Yale University Press.
Sibley, C. G. and Monroe, B. L., Jr. (1993) A supplement to distribution and taxonomy of birds of the world.
New Haven and London: Yale University Press.
Singh, S., Kothari, A. and Pande, P., eds. (1990) Directory of national parks and sanctuaries in Himachal
Pradesh: management status and profiles. New Delhi: Indian Institute of Public Administration.
Whistler, H. (1926a) A note on the birds of Kulu. J. Bombay Nat. Hist. Soc. 31: 458-485.
Whistler, H. (1926b) The birds of Kangra District, Punjab. Ibis (12)2: 521-581.
Williams, C. T. and Delaney, S. N. (1986) Migration through the north-west Himalaya - some results
of the Southampton University Ladakh expeditions, 2. Bull. Oriental Bird Club 3: 1 1-16.
Wynter-Blyth, M. A. (1952) A naturalist in the north-west Himalaya. J. Bombay Nat. Hist. Soc. 50: 559-
572.
Anthony J. Gaston, Canadian Wildlife Service, 100 Gamelin Boulevard, Hull, Quebec K1A 0H3, Canada
Peter J. Garson, Department of Agricultural and Environmental Science, University of Newcastle, Newcastle-
upon-Tyne NE1 7RU, U.K.
Sanjeeva Pandey, Wildlife Institute of India, Post Box 18, Chandrabani, Dchra Dun 248 001, India
54
A. J. GASTON, P. J. GARSON and SANJEEVA PANDEY
Forktail 9
Table 1. Birds seen in or near the Great Himalayan National Park.
Names and species order follow Sibley and Monroe (1990 and 1993). Key: * = species recorded in the
Park; (*) = recorded on approaches only; N= evidence of breeding seen; S= seen and heard singing
(indicating probable breeding); K = only reported by B. King (in litt., 1984).
SPECIES
Snow Partridge Lenea leruia
Himalayan Snowcock Tetraogallus himalayensis
Chukar Alecioris chukar
Black Francoun Francolinus francolinus
Hill Partridge Arborophila torqueola
Western Tragopan Tragopan melanocephalus
Koklass Pheasant Pucrasia macrolopha
Impeyan Monal Lophophorus irnpejanus
Kauj Pheasant Lophura leucomelanos
Cheer Pheasant Catreus wallichii
Speckled Piculet Picuntnus innominatus
Brown-fronted Woodpecker Dendrocopos auriceps
Himalayan Woodpecker Dendrocopos himalayensis
Scaly -bellied Woodpecker Picas squamatus
Great Barbet Megalaima virens
Eurasian Hoopoe Upupa epops
Pied Cuckoo Oxylophus jacobinus
Large Hawk-Cuckoo Cuculus sparverioides
Indian Cuckoo Cuculus micropicrus
Common Cuckoo Cuculus canorus
Oriental Cuckoo Cuculus saiuratus
Rose-ringed Parakeet Psittacula krameri
Slaty-headed Parakee t Psittacula himalayana
Himalayan Swiftlet Coltocalia brevirostris
White-throa ted Needletaii. Hirundapus caudacutus
Fork-tailed Swift Apus pacificus
Mountain Scops-Owl Otus spilocephalus
Rock Eagle-Owl Bubo bengalensis
Tawny Owl Slri.x aluco
Collared Owlet Glaucidium brodiei
Short-eared Owl Asio jlammeus
Grey Nightjar Caprimulgus indicus
Rock Pigeon Columba livia
Snow Pigeon Columba leuconota
Speckled Wood-Pigeon Columba hodgsonii
Oriental Turtle-Dove Streptopelia orientalis
Eurasian Collared-Dove Streptopelia decaocto
Wedge-tailed Green-Pigeon Treron sphenura
Eurasian Woodcock Scolopax rusticola
Solitary Snipe Gallinago solitaria
Lammergeier Gypaetus barbatus
Himalayan Griffon Gyps himalayensis
Northern Harrier Circus cyancus
Eurasian Sparrowhawk Accipitcr nisus
Northern Goshawk Accipiter gentilis
Buzzard Buteo sp., probably B. buteo
Black Eagle Ictinaetus malayensis
YEAR
1980 1983 1984-1985 1991
(*)
S
S
s
s
(*)
(*)
(*)
(*)
(*)
s
1994
Birds recorded in the Great Himalayan National Park
55
Golden Eagle Aquila chrysaetos
Booted Eagle Hieraaetus pertnatus
Eurasian Hobby Falco subbuteo
Common Kestrel Falco tinnunculus
Eurasian Jay Garrulus glandarius
Gold-billed Magpie Urocissa Jlavirostris
Grey Treepie Dendrocitta formosae
Spotted Nutcracker Nucifraga caryocatactes
Red-billed Chough Pyrrhocorax pyrrhocorax
Yellow-billed Chough P\>rrhocorax graculus
Large-biiled Crow Corvus macrorhynchos
Common Raven Corvus corax
Eurasian Golden-Oriole Oriolus oriolus
Long-tailed Minivet Pcricrocotus ethologus
Yellow-beujed Fantail Rhipidura hypoxanlha
White-throated Fantail Rhipidura albicollis
Black Drongo Dicnirus macrocercus
Ashy Drongo Dicrurus leucophaeus
Brown Dipper Cinclus pallasii
Chestnut-beijjed Rock-Thrush Monticola rufiventris
Blue Rock-Thrush Monticola solitarius
Blue Whistling-Thrush Myiophonus caeruleus
Plain-backed T hrush Zoothera mollissima
Scaly Thrush Zoothera dauma
Long-billed Thrush Zoothera monticola
White-collared Blackbird Turdus albocinctus
Grey-winged Blackbird Turdus boulboul
Eurasian Blackbird Turdus merula
Chestnut Thrush Turdus rubrocanus
Mistle Thrush Turdus viscivorus
White-browed Shortwing Brachypteryx montana
Dark-sided Flycatcher Muscicapa sibirica
Asian Brown Flycatcher Muscicapa dauurica
Rusty-tailed Flycatcher Muscicapa mficauda
Rueous-gorgeted Flycatcher Ficedula strophiata
Little Pied Flycatcher Ficedula westermanni
Ultramarine Flycatcher Ficedula superciliaris
Slaty-blue Flycatcher Ficedula tricolor
Verditer Flycatcher Eumyias thalassina
Rupous-belued Niltava Niltava sundara
Blue-throated Flycatcher Cyornis rubcculoides
Grey-headed Canary-Flycatcher Culicicapa ceylonensis
Orange-flanked Bush-Robin Tarsiger cyanurus
Golden Bush-Robin Tarsiger chrysaeus
Blue-capped Redstart Phoenicurus caeruleocephalus
Black Redstart Phoenicurus ochruros
Blue-fronted Redstart Phoenicurus frontalis
White-capped Water- Redstart Chaimarromis leucocephalus
Plumbeous Water-Redstart Rhyacomis fuliginosus
Little Forktail Enicunts scouleri
Spotted Forktail Enicurus maculatus
Siberian Stonechat Saxicola maura
Grey Bushchat Saxicola ferrea
Common Myna Acridotheres tristis
Jungle Myna Acridotheres fuscus
{*)
(*)
(*)
(*)
(*)
(*)
*
N
(*)
S
S
s
s
(*)
s
s
s
(*)
(*)
(*)
K
(*)
(*)
K
(*)
56
A. J. GASTON, P. J. GARSON and SANJEEVA PANDEY
Forktail 9
1994
Birds recorded in the Great Himalayan National Park
57
White Wagtail Motacilla alba
Grey Wagtail Motacilla cincrea
Tree Pipit Anthus trivialis
Olive-backed Pipit Anthus hodgsoni
I Rosy Pipit Anthus roseatus
Upland Pipit Anthus sylvanus
F Rufous-streaked Accentor Prunella hirnalayana
f Rufous-breasted Accentor Prunella strophiata
' Scaly-breasted Munia Lonchura punctulata
; Fire-fronted Serin Serinus pusillus
YEixow-BREAsrED Greenfinch Carduelis spinoides
European Goldfinch Carduelis carduelis
Plain Mountain-Finch Leucosticte nemoricola
Spectacled Finch Callacanthis burtoni
Dark-breasted Rosefinch Carpodacus nipalensis
I Common Rosefinch Carpodacus erythrinus
Pink-browed Rosefinch Carpodacus rodochrous
• Red Crossbill Loxia curvirostra
Brown Bullfinch Pyrrhula nipalensis
Orange Bullfinch Pyrrhula aurantiaca
■ Red-headed Bullfinch Pyrrhula erythrocephala
Black- and- yellow Grosbeak Mycerobas icterioides
Collared Grosbeak Mycerobas affinis
' Spot-winged Grosbeak Mycerobas melanozanthos
White-winged Grosbeak Mycerobas camipes
1 Rock Bunting F.mberiza cia
N
S
S
(*)
(*)
(*) (*)
(*)
K
S
(*)
(*)
(*)
58
A. J. GASTON, P. J. GARSON and SANJEEVA PANDEY
Forktail 9
1994
FORKTAIL 9 (1993): 59 - 82
59
The ecology of river birds in Nepal
DR STEPHANIE J. TYLER and DR STEPHEN J. ORMEROD
Five weeks were spent in Nepal in November and December 1991 and a further three weeks in March
and early April making a preliminary investigation of the ecology of river birds. Field work was carried
out on selected stretches of rivers from c. 200 m to over 3,500 m.
Data were collected on the distribution, use of the river corridor, feeding behaviour and diet of Brown
Dippers Cmclus pallasii, Grey Wagtails Motacilla cinerea, four species of forktail Enicurus, Plumbeous
Water- Redstarts Rhyacomis fuliginosus , White-capped Water-Redstarts Chaimarromis leucocephalus,
Blue Whistling-Thrushes Myiophonus caeruleus and several species of kingfisher. Data on biometrics of
some of these species were also obtained, and any aggressive interactions between species noted.
Species diversity in the winter months was highest at altitudes between 600 m and 1,600 m, with few
riverine species noted above c. 2,300 m. Plumbeous and White-capped Water-Redstarts were the most
numerous species, the former occurring at densities of a bird per 50-60 m on rivers in die Middle Hills.
Some evidence was obtained for differences in the use of river habitats by male and female Plumbeous
Water-Redstarts. Brown Dippers were in pairs and nest-building during November in the Middle Hills.
By March, Brown Dippers and other river birds had returned to breed on high altitude rivers; Brown
Dippers were still nest-building at over 3,000 m but pairs were feeding young in the lower Langtang.
In the winter Brown Dippers, Little Forktails Enicurus scouleri , White-capped Water-Redstarts and
Plumbeous Water-Redstarts occurred predominantly on rocks in the river. However, of these four
species only Brown Dippers were frequently recorded wading, swimming and diving in the river. White-
capped Water-Redstarts favoured rocks at the edges of rivers and also often occurred on riparian ground.
Spotted Enicurus maculatus. Slaty-backed E. schistaceus and Black-backed Forktails E. immaculatus were
recorded mainly on marginal rocks or shoals or wading at the river’s edge, with Black-backed Forktails
in particular often noted in riparian vegetation.
When foraging, Brown Dippers mainly caught prey from submerged rocks or the river bed, whereas
Little Forktails picked prey from spray-drenched rocks at waterfalls or from the hygropetric area (the
wetted zone) of rocks. Plumbeous Water-Redstarts predominantly used aerial flycatching as a foraging
technique. Both White-capped Water-Redstarts and Grey Wagtails also flycatched, but also spent much
time picking prey from shoals or mud or from riparian ground. Spotted and Slaty-backed Forktails
picked much prey from along the edges of the river, both from the river bed and from the mud or
vegetation at the river margins. Leaf- and stone-turning were frequent strategies. Most observations of
foraging Black-backed Forktails were of them picking prey from rocks and from shoals, muddy river
margins and riparian ground.
Measurements and weights of 20 Plumbeous Water-Redstarts and smaller numbers of ten other species
of river bird are presented. These are discussed in relation to the birds’ use of the river corridor and their
foraging behaviour.
Few instances of intra- or inter-specific aggression were noted, but Plumbeous Water-Redstarts
appeared to be particularly aggressive towards other river birds.
Possible implications of land use changes for river birds are discussed in the light of these observations.
It is suggested that Brown Dippers may be adversely affected on rivers in the Middle Hills by
deforestation, ploughing and resulting siltation and by the restricted flows due to the diversion of water
for irrigation. Spotted, Slaty-backed and Black-backed Forktails which require bankside trees or dense
riparian vegetation, are likely also to suffer from deforestation.
60
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
INTRODUCTION
There is much concern among conservationists throughout the world about
the impact on communities of terrestrial birds and other wildlife of land use
changes, notably the removal of natural forest cover by man to grow crops or
graze stock. Inskipp ( 1 989) has described the threats to birds from deforestation
in Nepal, whilst Ormerod (1990) has drawn attention to the subsequent
impacts on riverine ecosystems. He also made some preliminary observations
on bird communities on rivers in the Middle Hills and terai.
The river bird community in the Himalaya and Middle Hills in Nepal is
particularly diverse, including Brown Dippers Cinclus pallasii, Grey Wagtails
Motacilla cinerea , four species of forktail Enicurits, Plumbeous Water- Redstarts
Rhyacomis fuliginosus and White-capped Water-Redstarts Chaimarromis
leucocephalus. Little is known, however, of the impact of land use changes on
these species.
A large scale research project on water, erosion and land management,
funded by the Overseas Development Administration (ODA), is currently
being undertaken in catchments of the middle hills of Nepal by the Royal
Geographical Society, the Institute of Hydrology and various universities.
The aim is to investigate the physical, chemical and biological changes in
rivers from catchment perturbations; it involves comparisons between sub¬
catchments of a major river system, the Likhu Khola, which are subject to
different land uses. It was thought useful to carry out ornithological work on
the same catchments being studied for the ODA project so that opportunistic
use could be made of the available data on river quality and aquatic biota. The
aim of the ornithological study was to investigate the ecological requirements
of river bird species and, hence, better predict the wider effects of land use
changes such as erosion, sedimentation and habitat modification.
Preliminary data on habitat use and foraging behaviour of some river birds
in the Likhu Khola and in the Langtang area, the Kathmandu Valley and in
the Royal Chitwan National Park are presented here. These data were
collected during a 30 day period from 8 November to 1 1 December 1 99 1 and
during three weeks in late March and early April 1992. They indicate some
of the likely impacts on birds of land use changes, but it is emphasised that
further data are needed over a longer period of time and from other seasons
of the year before there can be an adequate understanding of the impacts.
STUDY AREA AND METHODS
The main study area covered 3 km of the Likhu Khola (600-700 m), a river
lying 25 km north of Kathmandu (27"50’N 85°20’E), and draining into the
Trisuli River and thence the Narayani and the Ganges (Fig. 1). This area
1994
The ecology of river birds in Nepal
61
Figure 1. Sketch of central Nepal showing the location of the Langtang Khola, Trisuli Khola, Likhu
Kola, Bagmati River and the Narayani River.
included 1-2 km stretches of seven tributaries, the Mahadev and Dee Khola
to the north, and the Bhondare and Jogi, the Bore Khola, Syalping and
Ghyambe Khola to the south (Fig. 2). Land use in the Likhu Khola is
predominantly arable farmland, with rice the main summer crop and cereals
grown as a winter crop. Terraces adjoin the main river and tributaries for
much of their length, with many irrigation ditches diverting water from the
streams onto the small fields. The steepest banks along the river still support
trees and scrub, with patches of degraded Sal Shorea robusta forest in a few
62
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
areas. Alder Alnus nepalensis fringes some streams, but felling for fuel and
timber has reduced these in most places to a sparse scattering. The tributary
streams have a steep gradient, and are rocky with frequent waterfalls.
Descriptions of each are given in Appendix 1, but a common characteristic
in both the winter and spring visits was an accumulation of gravel, sand and
silt on the stream bed, and a much reduced flow due to diversion of water for
irrigation.
Additional data were collected opportunistically during both visits in the
Langtang Himal from a short stretch of the Trisuli Khola at c. 1,600 m, from
the Trisuli River between Dhunche and Syabrubesi (c. 1,200-1,600 m) and
from sections of the Langtang Khola from its junction with the Trisuli at
Syabrubesi up through oak Quercus/ Rhododendron forest to Kyangin Gompa
above Langtang (c. 3,700 m) (Fig. 1). Data were gathered also from three
1 km stretches of the Bagmati River in the Kathmandu Valley:
1 . A rocky, Alder-lined, fast-flowing stretch ( 1 5-20 m wide) at Sundarijal,
upstream of Kathmandu, at an altitude of c. 1,450 m;
2. A slower, open stretch (10-20 m wide) with shingle beds and vertical
sand banks, downstream of Sundarijal;
3. A heavily organically polluted slower-flowing and braided section (up to
50 m) below the Chobar Gorge (c. 1,200 m) downstream of the city).
They were also gathered from various stretches of the Narayani (up to 400
m in width), the Reu and small forest streams in the Royal Chitwan National
Park at 200-250 m (Fig. 1).
The distribution of river birds on all these watercourses was assessed both
in the winter and in the spring study periods, by walking (or in the case of the
Narayani drifting in a boat) along each section. Data were also collected on
bankside habitats, river or stream width and the general nature of the
watercourse (e.g. presence of rocks, shoals, riffles etc.).
The location of each bird in the river corridor was noted i.e. whether in the
mid-river, marginal (within 1 m of the bank) or riparian zone, the last defined
as that area of rock, grassland or woodland up to 10 m from the river bank,
and whether in the water, on mid-river or marginal rocks, shoals or mud, in
trees or other vegetation. During observations of individual birds, each time
they moved, their new location was recorded.
The foraging behaviour of nine species of river bird was recorded in various
categories: picking prey from rocks, shoals, mud, riparian ground or
vegetation; flycatching; catching prey on or in water or the river bed when
swimming, diving or wading. Faecal samples, where these could be definitely
attributed to a particular species, were collected and stored in alcohol for later
analysis of invertebrate or other prey; some opportunistic observations were
also made of the prey taken by different river birds.
1994
The ecology of river birds in Nepal
63
Figure 2. Likhu Kola catchment showing area covered in this study.
All interactions between birds, both intra- and inter-specific, were noted.
To obtain some data on biometrics, a sample of birds was caught in mist-
nets erected across tributaries of the Likhu Khola and across the Trisuli
Khola and Langtang Khola. Each bird was weighed (+ 0.1 g) by spring
balance, and the length of wing to + 0.5 mm (maximum flattened chord),
tarsus to 0.1 mm (using the method described by Schmid and Spitznagel
(1985), bill (tip to feathering), bill to skull (tip of bill to hind skull) and depth
of bill (above the nostrils) to + 0.5 mm were measured.
RESULTS
Distribution
1. The Likhu Khola
a) Winter period
Over twenty species of river bird were recorded in the Likhu Khola catchment.
In addition to those species listed in Table 1, Indian Pond-Herons Ardeola
grayii, Little Egrets Egretta garzetta, Cattle Egrets Bubulcus ibis, Black Storks
Ciconia nigra and Woolly-necked Storks C. episcopus, Red-wattled Lapwings
Vanellus indicus, Common Sandpipers Tringa hypoleucos and Green Sandpipers
64
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
T. ochropus and Plain Martins Riparia paludicola were all frequent. The most
numerous river passerines were Plumbeous Water-Redstarts and White-
capped Water-Redstarts. Only two pairs of Brown Dippers and two single
birds were seen here. They were on the main river and on the Syalping Khola,
the largest of the tributaries surveyed (Fig. 3a). Grey Wagtails were widespread
(Fig. 3a).
Plumbeous Water- Redstarts occurred at densities of one bird per 50-60 m
along the open main river, males greatly outnumbering females (by 10: 1). By
contrast, on the well-wooded Bore Khola and on some other tributaries,
females were predominant (Figs. 3b and c). White-capped Water Redstarts
occurred commonly on the main river and more open south-facing tributaries
(Fig. 4a). Little Forktails Enicurus scouleri were scarce, although three birds
were recorded in 1 km of the Mahadev Khola, where there was a narrow gorge
with numerous waterfalls and wet rock faces (Fig. 4b). One pair of Spotted
Forktails E. maculatus was seen regularly on a shoal in the Likhu Khola, with
a third bird on the Syalping (Fig. 4b) . The scarcer Black-backed E. immaculatus
and Slaty-backed Forktails E. schistaceus both occurred only on wooded
sections of tributaries, even on very narrow (1 m wide) wooded side streams
(Fig. 4c). Blue Whistling-Thrushes Myiophonus caeruleus were frequently
seen by water but usually flew off when disturbed into trees or up the valley
sides. Three Blue Rock-Thrushes Monticola solitanns were also seen by the
main river and by the Dee Khola, where a Wallcreeper Tichodroma muraria
was noted on streamside rocks. Both Common Kingfishers Alcedo atthis and
Crested Kingfishers Megaceryle lugubris were seen on three or four occasions
on the main river and the Syalping, with the former species also on the narrow
Bhondare. White-throated Kingfishers Halcyon smymensis were seen twice
by water but were often away from watercourses over fields.
b) Spring period
By late March there were very few Plumbeous Water-Redstarts in the Likhu
Khola (Table 1). About 5 km downriver below the confluence with the
Tadhu Khola, near Dhikuri, a pair was feeding three recently fledged young
on 27 March, indicating a laying date in late February, earlier than noted by
Inskipp and Inskipp (1991). The other main differences between the two
visits were the small numbers of White-capped Water Redstarts and the
paucity of forktails, with only Slaty-backed seen during the spring survey
(Table 1).
2. Himal Langtang, Kathmandu Valley and Chitwan.
a) Winter period
On a short stretch (200 m) of the Trisuli Khola, Plumbeous Water- Redstarts
were the most frequent species, although were scarce on the 100 m wide
1994
The ecology of river birds in Nepal
65
Table 1. Numbers of 14 species of riverbird observed in the Likhu Khola study area in November 1991
and late March 1992. Figures in parentheses for Plumbeous Water-Redstart refer to the number of
males.
Trisuli River and on the Langtang Khola (T able 2) . Brown Dippers were only
seen on the Trisuli Khola; above 2,000 m there were only a few Plumbeous
Water-Redstarts, two Spotted Forktails and a Blue Whistling-Thrush
(Table 2).
By contrast, at the lower altitude of the Bagmati River near Sundarijal,
there was a good diversity of species. Here Plumbeous Water-Redstarts were
at the highest densities, with males predominating (Table 2, Fig. 5).
Downriver of this stretch, where the gradient declined and the river meandered
across a broad, open valley, Common Sandpipers, Little Ringed Plovers
Charadrius dubius, White Wagtails Motacilla alba and Plain Martins replaced
the species of the rocky, turbulent rivers (Table 2). On the Bagmati below
Kathmandu, both Plumbeous and White-capped Water-Redstarts occurred
in small numbers in the Chobar Gorge and on marginal rocks immediately
downriver, but the bird community on this grossly polluted river was
dominated by sandpipers and wagtails, as well as by Indian Pond-Herons and
both Little and Cattle Egrets (T able 2) . Thus on 1 0 and 20 November, there
was a large flock of Green Sandpipers with smaller numbers of Wood T.
glareola and Common Sandpipers, one Common Redshank T. totanus, three
White-breasted Waterhens Amaurornis phoenicurus, a flock of over 40 Grey¬
headed Lapwings Vanellus cinereus and a Northern Lapwing V. vanellus,
numerous White Wagtails, 5 White-browed M. madcraspatensis and at least
2 Grey Wagtails.
66
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
Figure 3. Distribution of three species of river birds in November 1991 in the Likhu Kola,
a) Brown Dippers and Grey Wagtails; b) male Plumbeous Water-Redstarts; c) female Plumbeous
Water- Redstarts .
1994
The ecology of river birds in Nepal
67
Figure 4. Distribution of five species of river birds in November 1991 in the Likhu Kola,
a) White-capped Water-Redstarts; b) Spotted (large dots) and Little Forktails (small dots);
c) Black-backed (large dots) and Slaty-backed Forktails (small dots).
68
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
Chironomid midge larvae, characteristic of organic pollution, were abundant
in the black mud at the river edge. It is of note that a greater number of birds,
albeit migrants, were recorded on this polluted river than on any other stretch
of similar length.
In Royal Chitwan National Park, only Grey Wagtails, Black-backed
Forktails and Common Kingfishers were seen along the narrow forest
streams, although two Blue-eared Kingfishers Alcedo meninting and another
Common Kingfisher were observed at Tiger Tops at the edge of forest by an
ox-bow lake. Common and Pied Kingfishers Ceryle riidis were commonly
seen on the Reu and Narayani, and at ox-bows, where four Stork-billed
Kingfishers Pelargopsis capensis were also observed (Table 3). One Crested
Kingfisher was noted on the Reu, whilst a White-capped Water-Redstart was
seen on a marginal boulder in a 4 km stretch of the Narayani River, with four
Plumbeous Water-Redstarts also on this stretch and another on a tributary.
b) Spring
By late March in the Himal Langtang many altitudinal migrants had moved
back up to their breeding grounds (Table 2). Thus Brown Dippers were
distributed from the T risuli River below Syabrubesi to above Langtang. T wo
pairs of dippers at lower altitudes were feeding young, whereas a pair between
Langtang and Kyangin Gompa above 3,000 m were still nest-building. Grey
Wagtails, White-capped Water-Redstarts and Little Forktails were all seen
above 2,500 m, with Spotted Forktails frequent along the Langtang Khola.
Few river birds were noted above 3,000 m.
On the Bagmati River at Sundarijal, Plumbeous Water-Redstarts, many in
pairs and nest-building, were still common but other river species were now
scarce or absent (Table 2). Flows were very low, with the river reduced to a
trickle. The downriver slower-moving stretch supported similar species to
those seen in the winter, but Little Ringed Plovers were now nesting (and
Red-wattled Lapwings mating).
In the Chitwan lowlands kingfishers (Common, Pied, Stork-billed and
White-throated) were still common along streams and rivers in early April,
but only one Grey Wagtail (on a forest stream) and one White-capped Water-
Redstart (on the Narayani) were seen. Herons, egrets, waders and other
species of wagtail (flava , alba and maderaspatensis) were numerous.
Ecological segregation of river birds
a) Altitudinal preferences
The winter observation of a Blue Whistling-Thrush by a small stream at
Kyanjing Gompa, at c. 3,750 m, is apparently unusual (Inskipp and Inskipp
1991). Other river birds were scarce during the winter survey period above
c. 2,300 m, with only a few Plumbeous Water-Redstarts and Spotted
1 094
The ecology of river birds in Nepal
69
Table 2. Numbers of 16 species of river bird seen in the winter and spring surveys on stretches of river
in the Langtang area and Kathmandu valley. (The Whistling-Thrush on the Langtang Khola above
3,200m was on a tributary'.
E S o
E E
CO O ro -T-
E S
E E
E E
II
oo 'T—
S E
.i= CO 1 CO CM t—
+ in cm
cm in r--
CM CM Oi to
rr cm in ■*— co t— co
■vF — co
in i"- m t— co
co in cm co
in in
o p
^ O
5 &
~ ~ >S
~ E
jd a .t; ™
70
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
Forktails at these high altitudes. Abundances of the redstarts were much
greater at altitudes of 600-1,500 m compared with either 2,000 m or 200 m
(Tables 1 and 2). Brown Dippers and Little Forktails were only noted
between 600 and 1 ,600 m, whereas Grey Wagtails were widespread from 200
to over 1,500 m. Black-backed Forktails occurred alongside Slaty-backed
and Spotted Forktails in the Likhu Khola up to 1,000 m, but unlike these
species, were not seen above this altitude but did occur in the lowlands. Of
the Enicurus, only Spotted Forktails were observed over 1,600 m.
In the spring Grey Wagtails, Brown Dippers and both Plumbeous and
White-capped Water-Redstarts were widespread at higher altitudes, although
only one White-capped Water-Redstart, one wagtail and three dippers were
seen above 3,200 m. The forktails were more clearly segregated than in the
winter with Little and Spotted from 1,600 to nearly 3,000 m, Slaty-backed
in the Likhu Khola at 600 to 900 m and Black-backed in the Chitwan
lowlands.
b) Flabitat use
Both Plumbeous and White-capped Water-Redstarts commonly perched on
top of large rocks or boulders in the river, with the latter species preferring
marginal rocks and riparian ground, sometimes 1 00 m or more away from the
river (Table 3). Little Forktails and Brown Dippers were also frequently seen
on mid-river or marginal rocks, but these species generally occurred on small
rocks, often drenched with spray or close to the water edge. Both these
species commonly waded, although only dippers swam and dived (Table 3).
The other three species of forktail preferred marginal habitats, creeping
amongst boulders, or wading at the water’s edge on mud and shoals. The
small number of observations preclude any realistic comparison of habitat
Table 3. Use of the river corridor by nine species of bird as shown by the proportion of observations of
each species in different locations.
1994
The ecology of river birds in Nepal
7]
use between these birds, although Black-backed Forktails were only seen in
wooded sections of tributaries of the Likhu Khola and on forested streams in
Chitwan National Park. This species spent more time in riparian habitats
than Slaty-backed or Spotted Forktails. In the Likhu Khola catchment in the
winter, the few Spotted Forktails observed were in more open habitat than
the Slaty-backed Forktails but, at Sundarijal on the Bagmati, both occurred
together on the alder-lined section (Fig. 5). On the Langtang Khola Spotted
Forktails, if disturbed, flew into thick riparian vegetation, a habit shared with
Slaty-backed Forktails.
Grey W agtails occurred in all locations, including habitats away from rivers
e.g. on roads and tracks, and on rice stubble on terraces. By rivers they
generally occurred along the margins or on damp riparian grassland.
c) Feeding behaviour
A diversity of feeding strategies was shown by the nine species of river bird
for which data were collected during the winter period. Although some
strategies were common to all or most species, there were some clear
differences between species (T able 4) . Thus flycatching was the predominant
foraging strategy (75% of observations) used by Plumbeous Water- Redstarts.
These small birds often perched high on a boulder and flew up almost
vertically to catch an insect. Aerial sallies up to 5 m or more above the water
were not uncommon, although most aerial flights (74%) were lower than 2
m. Birds usually caught insects over water but sometimes flew over riparian
vegetation (c. 8% of aerial flights), even hovering briefly to pick an insect off
a leaf. Most prey appeared to be small insects such as chironomid midges, but
larger prey were also taken (see Diet section below). Other species, notably
Grey Wagtails, White-capped Water-Redstarts and Slaty-backed and Black-
backed Forktails, also used flycatching as a foraging method, but to a lesser
extent than the redstarts. White-capped Water-Redstarts foraged commonly
by picking prey from the ground or from vegetation in the riparian zone (40%
of observations) as well as by picking prey from rocks (40%) (Table 4).
Only Brown Dippers foraged by swimming and diving as well as wading
(95% of observations) but Grey Wagtails and all four species of forktail,
particularly Slaty-backed and Spotted, picked items from shallow water
whilst wading. Little Forktail spent most time picking prey from wet rocks
and waterfalls, often drenched by spray. Pecking rates of Little Forktails were
high, 80-124 pecks per minute, with a bird sometimes feeding on one small
rock for five minutes or more and picking more than 400 items from the wet
rock surface. Observations revealed many dipterans, small caddis larvae
(Trichoptera) and mayfly nymphs (Ephemeroptera) in these areas. Whilst
the three larger forktails all mainly fed in the marginal zone, picking items
from the water, from rocks, shingle or mud, or turning over leaves to find
72
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
Table 3. Foraging techniques of nine species of river bird in Nepal shown by percentage of total
observations: N Number of observations; 1 Catching prey in or on water or on river bed; 2 Picking prey
from rocks; 3 Picking prey from shoals or mud; 4 Picking prey from riparian ground or vegetation; 5
Aerial flycatching.
prey, only the Spotted was seen to frequently turn over stones and to foot-
paddle to disturb and find prey. This species often picked up large items such
as cased caddis larvae, and then had to pause to beat the prey repeatedly to
kill it or extract it from its case. In fewer instances Little and Slaty-backed
Forktails also dealt with caddis larvae, molluscs or large worms (Oligochaeta)
in this way.
Few data were collected on the foraging behaviour of Blue Whistling-
Thrushes which, when disturbed, tended to fly off into trees or away from the
river. This species was less confined to the river corridor than the other river
birds studied in this project although, as mentioned above, White-capped
Water-Redstarts and Grey Wagtails also foraged away from watercourses.
Even Plumbeous Water-Redstarts sometimes foraged in riparian vegetation.
Because flycatching in the river corridor is a much more conspicuous
foraging method, the true extent of vegetation gleaning may have been
overlooked . Notably, Plumbeous W ater- Redstarts when disturbed, frequently
took cover in trees and scrub away from the river.
d) Diet
Faecal pellets collected from the Likhu Khola are still to be analysed, but
observations suggested that all nine species of bird took invertebrate prey.
Differences between species in their choice of prey were evident with, for
example, Plumbeous Water-Redstarts taking more adult winged insects and
Brown Dippers and Little Forktails feeding almost exclusively on aquatic
larval or nymphal stages of insects e.g. mayfly nymphs, caddis larvae and
blackfly larvae Simulium (Diptera). Size differences in prey taken by different
1994
The ecology of river birds in Nepal
73
Figure 3. Distribution of some river birds at Sundarijal in November 1991 (not to scale),
a) Slaty-backed Forktail (closed circle) and Spotted Forktail (star); b) male Plumbeous Water-Redstart
(closed circle) and female Plumbeous Water-Redstart (white star in closed circle); c) White-capped
Water-Redstart (closed circle); d) Grey Wagtail (star).
74
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
species were also evident. Thus Plumbeous Water-Redstarts preyed on a
wide range of insects and from a diversity of orders e.g. large dragonflies
(Odonata), butterflies (Lepidoptera), bees (Hymenoptera), but mainly small
flies and midges (Diptera: Chironomidae, Simuliidae). Little Forktails took
numerous tiny items of prey, sometimes spending 5- 1 0 minutes picking prey
from an algal web on the upstream side of a wet rock. Invertebrates in these
situations included dipteran larvae and small caddis larvae and mayfly
nymphs. Brown Dippers and the three larger species of forktail frequently
took much larger items, which then involved considerable handling time
(beating).
Berries were eaten from riparian vegetation by Plumbeous Water-Redstarts
and, from the nature of their faeces, probably also by White-capped Water-
Redstarts and Blue Whistling-Thrushes.
e) Biometrics
Weights and measurements of the small sample of river birds caught in mist
nets indicated considerable overlap between species in size and weight
(Table 5). Excluding the two species of Alcedo kingfishers, Plumbeous
Water-Redstarts and Little Forktails were the smallest species of river bird in
all measurements; moreover, the weights and measurements of these two
species were very similar. Grey Wagtails differed only in their longer bills and tails.
Brown Dippers and White-capped Water-Redstarts were also rather
similar in wing and tarsus length but the dippers had longer, stouter bills,
shorter tails and were twice the weight of the chats. Slaty-backed and Black-
backed Forktails differed little from each other, and also resembled White-
capped Water-Redstarts apart from their much longer tails (x 2 those of the
chats), longer bills and shorter tarsi.
The single first year Brown Dipper had a wing of 92 mm, shorter than that
of any of the adults caught (95-99 mm). Young White-throated Dippers
Cinclus cinclus in Wales also have shorter wings than adults (Ormerod and
Tyler 1986). Likewise, wing length of the first year Plumbeous Water-
Redstarts (mean 73 mm, n=17) and White-capped Water- Redstarts (88.2
mm, n=3) were significantly smaller than older birds (79.2 mm, n=3; 95.4
mm, n=l 1).
f) Interactions between species
The high density of birds along some rivers inevitably resulted in birds
sometimes being in close contact. With the exception of the Brown Dippers
some of which were in pairs and nest-building in November, and Spotted
Forktails, also mainly in pairs at this time, other river birds appeared to be
holding individual territories during the winter study. A few instances of
intra-specific aggression, especially between Plumbeous Water- Redstarts
1994
The ecology of river birds in Nepal
75
Table 2. Biometrics of 1 1 species of river bird caught in Nepal in November/December 1991 . Ranges
of weights and measurements for each species are shown in parentheses.
and between White-capped Water-Redstarts, were observed (Table 6).
When two birds of the same species approached within 1-2 m of each other,
then chases ensued. Where male and female Plumbeous Water-Redstarts
occurred on the same stream, the aggressor was often the male, and the
subordinate bird a young female. Male redstarts also sang against each other.
One Little Forktail chased another of the species which was driven by the
observer into the former’s territory, whilst one of the pair of dippers on several
occasions chased off a third dipper. In general intra-specific aggression
appeared to be largely avoided through the spacing of birds along the watercourses .
Despite occasional aggression between species, the territories of two or
more different species frequently coincided or overlapped. Most instances of
inter-specific aggression related to a bird of a larger species chasing one of a
smaller species (Table 6). Individuals of Plumbeous Water-Redstarts and of
White-capped Water- Redstarts frequently perched within a few metres of
each other, but closer encounters often resulted in a short aerial pursuit, with
the latter flying after the former species. The large, dominant , White-capped
76
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
Table 6. Intra-and inter-specific interactions among six species of river bird in Nepal.
Water- Redstarts also chased Slaty-backed, Black-backed and Little Forktails.
Despite the Plumbeous Water-Redstart’s small size, it was a particularly
aggressive species, sometimes chasing Slaty-backed Forktails, Little Forktails
and Grey Wagtails when these birds were feeding 4-5 m away. On one
occasion a Plumbeous Water-Redstart pursued a Little Forktail repeatedly
until the forktail left the former’s presumed territory. One Plumbeous Water-
Redstart also chased off a Hodgson’s Redstart Phoenicurus hodgsoni which
was foraging close to the river bank, whilst a Blue Rock-Thrush behaved very
aggressively towards a White-capped Water-Redstart, the latter bird then
chasing away a Plumbeous Water- Redstart. No aggression was noted towards
or by Spotted Forktails even though other species fed in close proximity.
DISCUSSION
Distribution
Most river birds that spend the spring and summer in the Himalaya are
altitudinal migrants, moving down to the foothills or the terai in the autumn
(Ali and Ripley 1983, Fleming etal. 1984, Inskipp and Inskipp 1991). During
November and December those birds observed in the study areas were
therefore already on their lower wintering grounds, with very few birds
observed above 2,000 m (Table 2). The paucity of Brown Dippers wintering
at high altitudes in the Langtang valley is perhaps strange, given frequent
observations of this species above 2,500 m in Nepal in November and
December (e.g. Mycock and Calladine in litt., D. Pritchard in litt.). The Blue
Whistling-Thrush at Kyangin Gompa at 3,750 m was of particular note.
With the exception of Brown Dippers, which are known to breed during the
1994
The ecology of river birds in Nepal
77
winter when at low altitudes (Fleming et al. 1984), and Spotted Forktails,
river birds were not in obvious pairs during the winter study period.
Few White-capped or Plumbeous Water-Redstarts winter below 500 m
(Inskipp and Inskipp 1991) and so the records of a single of the former and
five of the latter species in Royal Chitwan National Park at c. 200-250 m are
of interest.
Plumbeous Water- Redstarts were the most numerous species in the Likhu
Khola catchment (Table 1, Figs. 3b and c) and the most widespread species
generally on fast-flowing, rocky rivers (Table 2, Fig. 5). A difference in
distribution of males and females was noted by Ali and Ripley (1983), who
found that the females and young birds wintered at lower levels than adult
males. This study provides little evidence of this, although at 600 - 1,450 m
in the Likhu Khola (Figs. 3b and c), and on the Bagmati river at Sundarijal
(Fig. 5), males outnumbered females, whilst four of the five redstarts seen in
the Chitwan lowlands were females. The most marked difference between
the distribution of sexes in this study was in their use of different habitats,
with males abundant on the wider rivers, and females more numerous on the
narrow, more wooded tributaries (Figs. 3b and c). By March most redstarts
had left the Likhu Khola. In May both Plumbeous and White-capped Water-
Redstarts are absent from the valley (R. Wyatt pers. comm.). If some
Plumbeous Water- Redstarts breed early in the spring as did the pair at
Dhikuri, is it possible that they breed again in their higher summering areas?
Of the forktails, only Black-backed occurred at very low altitudes, as
recorded previously. At 800-1,000 m Black-backed and Slaty-backed were
found in close proximity during the winter, as noted by Ali and Ripley (1983),
sometimes also alongside Spotted or Little Forktails. Only these two latter
species were seen at over 1,000 m. Whilst Inskipp and Inskipp (1991) noted
that Grey Wagtails wintered mainly below 365 m, this study showed them to
be widespread and not uncommon wintering birds at altitudes up to
1,500 m.
The limited data on the altitudinal distribution of kingfishers accord with
those of other observers, with Stork-billed, Pied and Blue-eared Kingfishers
being notably lowland species, and the others occurring over a wider range
of altitudes. The two Blue-eared Kingfishers were caught in an area at
Chitwan where this locally scarce species has previously been recorded
(Gurung 1983).
It was not the intention of this study to investigate birds on rivers with low
gradients. Data collected opportunistically did, however, show that species
diversity tended to be higher on such rivers, particularly at low altitudes
(Table 2).
Possible competition between species using the same general habitat has
been discussed by various authors (e.g. Diamond 1978, Schoener 1982).
78
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
Generally it appears that competition is avoided between closely related
species through differences in their use of the habitat, foraging behaviour and
diet, which may be reflected in differences in bill size, tail length or other
biometric features. Alternatively, an abundance of food may prevent
competition (Schoener 1982). Interference or exploitation competition may
occur amongst other less closely related species using the same habitat (Eadie
and Keast 1980, Hurlbert et al. 1986).
On those upland rocky fast-flowing rivers in Nepal between 800- 1 ,000 m,
there is, in the winter months, a concentration of migrant and resident species
of birds, all of which feed mainly on invertebrates. This study, albeit using
data collected over a very short period, demonstrates some differences in the
use of the river corridor by different species, in foraging methods, diet and
biometrics (Tables 3-5), suggesting how competition between species may
be avoided.
a) Segregation by body size and weight
Differences in the size of species, or in the size of their bills, suggest that they
exploit a different range of food resources and hence avoid competition. Our
biometric data for 1 1 species of river bird (Table 5) accord with those
obtained by other authors (Biswas 1961, Diesselhorst 1968, Rand and
Fleming 1 957, Ripley 1 950), and do show marked differences between most
species. A few species closely resembled each other in size and weight e.g.
Plumbeous Water-Redstart and Little Forktail; Brown Dipper and White-
capped Water-Redstart (Table 5), but these species pairs did show differences
in bill size and in their foraging methods. Thus the redstarts flycatched or
picked prey from riparian habitats or dry rocks, whilst the dippers and
forktails foraged in the water, from wetted rocks or the marginal zone. The
long, stout bill of the Brown Dipper enables it to probe amongst rocks and
stones on the river bed, whilst the long bills of the larger forktails may also
enable them to probe in mud and turn over leaves and stones.
b) Segregation by habitat, foraging behaviour and diet
Brown Dippers and Little Forktails appeared to be largely dependent on
large and small aquatic invertebrates respectively, from the river bed or on
midriver rocks, with the former species obtaining prey by diving, swimming,
wading or picking from rocks below the water surface, and the latter mainly
by picking from the hygropetric area on wetted rocks. White-capped and
Plumbeous Redstarts took numerous aerial stages of insects, of both aquatic
and terrestrial origin, by flycatching. The White-capped Water Redstarts also
spent much time feeding from marginal rocks and the riparian zone, whilst
the three larger forktails foraged extensively in the marginal zone, often where
there was thick streamside cover.
1994
The ecology of river birds in Nepal
79
Fleming et al. (1984) noted that White-capped Water Redstarts often
associate with Plumbeous Water- Redstarts. Whilst the two species commonly
occurred together in this study, even perching on the same or adjacent rocks,
they differed in the extent to which they used different parts of the river
corridor. Ali and Ripley (1983) found that White-capped Water- Redstarts
favoured wider rivers, avoiding the small rivulets favoured by Plumbeous
Water-Redstarts. Whether this was during the breeding season or on the
wintering areas is not clear. In this study the White-capped Water-Redstarts
avoided those narrow, wooded tributaries where female Plumbeous Water-
Redstarts predominated. There was no evidence, though, that the latter,
particularly the males, actually favoured small rivulets, as they occurred at
the highest densities on the 20-40 m wide Likhu Khola. Various authors have
noted the territoriality of wintering Plumbeous Water-Redstarts and their
aggression towards others of the same species, but Ali and Ripley (1983)
regarded them as being tolerant of White-capped Water-Redstarts and
forktails. Certainly in this study they were not aggressive towards the larger
redstart, rather the reverse, but did chase Little Forktails and other species
within their territory (Table 6).
Whilst few data were collected on forktails during this study, it was evident
that Little Forktails occurred on fast-flowing, turbulent stretches of river with
spray-drenched rocks or waterfalls. Stream width appeared unimportant,
with birds recorded on watercourses from only 6 m in width to 40 m, although
Ali and Ripley (1983) noted that, in the winter, wider rivers were used by this
species than in the summer. Ali and Ripley and Fleming et al. (1984) also
recorded the three larger species, particularly Spotted, as essentially birds of
small forest streams. Observations from this study confirmed this, although
it is of note that a pair of Spotted Forktails were observed on five days foraging
for long periods on a large shoal on a 40 m wide, almost treeless section of
the Likhu Khola. All three species were generally found in the marginal zone
where there was overhanging vegetation or thick riparian cover into which
they could fly when disturbed.
Implications for river birds of land use changes
Removal of bankside cover is likely to be detrimental to a number of species
of river bird, notably the three larger species of forktail, Plumbeous Water-
Redstarts and Blue Whistling-Thrushes. All these species use riparian trees
and shrubs for shelter and for food. The three larger forktails in particular,
and Plumbeous Water-Redstarts frequently take refuge from potential
predators in trees, shrubs and undergrowth; leaf litter in the riparian zone is
also a favoured feeding area for all the long-tailed forktails, whilst the
contribution of leaves and insects falling from bankside vegetation into the
water is important for many invertebrates and hence fish. The contribution
80
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
of insects and berries from vegetation in the diet of Plumbeous Water-
Redstarts (and probably White-capped Water- Redstarts and Blue Whistling-
Thrushes) may be important at some times of the year and should be further
evaluated. Ali and Ripley (1983) mention berries in the diet of both White-
capped and Plumbeous Redstarts, although refer to them as only occasionally
taken by the last species. In the Likhu Khola, female Plumbeous Water-
Redstarts were seen taking berries on at least ten occasions.
Brown Dippers were few in the Likhu Khola, being found only on the main
river and on the Syalping Khola, where there was a good flow of water.
Impacts on the tributaries through removal of bankside and hillside cover,
cultivation of hillsides and diversion of the water from the streams for
irrigation has made them unsuitable for birds which depend on large aquatic
benthic invertebrates. The results of invertebrate sampling in the tributaries
by the Catchment Group of the University of Wales College of Cardiff wall
be reported elsewhere, but preliminary results show that streams in areas of
agriculture have much more sand on their beds than streams in forest, and
differences in the aquatic insect community are also pronounced, caddis
larvae and mayfly nymphs being scarce in streams with thick sandy sediment
(Rundle, Jenkins and Ormerod in prep.). During the survey period, work by
local farmers on the irrigation channels frequently resulted in very high
sediment loads in the water in the tributaries. The turbidity in the water must
also affect the ability of dippers to see and catch prey.
Pollution was not a major ecological problem on the rivers studied, other
than on the lower Bagmati, which had a high input of sewage, as well as of
other pollutants from domestic and industrial sources in Kathmandu. Here
large aquatic invertebrates were absent but there were very high densities of
small invertebrates (midge larvae) . Species ofbirds, notably dippers, dependent
on invertebrate groups such as caddis were absent from the lower Bagmati,
but birds such as wagtails and sandpipers which could take advantage of the
dense food supply in the mud, occurred at higher densities here than at any
other observed stretch of river with similar gradient e.g. the stretch below
Sundarijal. There was also a good diversity of, mainly migrant, species on the
lower Bagmati, as recorded previously by Inskipp (1988) and others. Such
high diversity and density of birds has been noted on other organically
polluted rivers, as in Addis Ababa in Ethiopia (Tyler in press). The degree
of pollution of rivers in the Middle Hills from human faeces, pesticides and
fertiliser inputs is unknown, but is almost certainly considerable.
1994
The ecology of river birds in Nepal
81
We are grateful to the R.S.P.B. for approving and helping to fund the winter
work as part of S. J. Tyler’s sabbatical project, and to the Oriental Bird Club
for a grant to S. J. Tyler towards the spring surveys. We thank too Richard
Porter for his encouragement, in particular Carol Inskipp, Conservation
Officer of the Oriental Bird Club, for much useful advice, staff of the Parivar
Agency for all their cheerful support, company and hard work, particularly
Deshek Kafab Sherpa, his brother Keta, Pasang Sherpa, Dawa and Thaba,
and staff at Tiger Tops Jungle Lodge in Royal Chitwan National Park,
notably the excellent nature guide, Sukra Kumal. Thanks are due too to Dr.
Maskey and Mahendra Shrestha of the Department of National Parks and
Wildlife Conservation for their cooperation, to Dr Alan Jenkins of the
Institute of Hydrology at Wallingford for advice, to Simon Rundle, Roger
Wyatt and Clare Lloyd for help in the field during November, and to Sally
Tyler for her help and good company in the spring. Finally, Tim Inskipp’s
comments on a first draft of this paper are gratefully acknowledged.
REFERENCES
Ali, S. and Ripley, S. D. (1983) Handbook of the birds of India and Pakistan (compact edition). Delhi:
Oxford University Press.
Biswas, B. (1961) The birds ofNepal. Parts 3-5. J. Bombay Nat. Hist. Soc. 58: 100-134, 444-474, 653-
677.
Diamond,.!. M. (1978) Niche shifts and the rediscovery of interspecific competition. American Scientist
66: 322-331.
Diesselhorst, G. (1968) Beitrage zur Okologie der Vogel Zentral- und Ost-Nepals. Khumbu Nepal 2: 1-
417.
Eadie, J. McA. and Keast, A. (1982) Do Goldeneye and Perch compete for food? Oecologia (Berlin) 55:
225-230.
Fleming, R. L. Sr., Fleming, R. L. Jr. and Bangdel, L. S. (1984) Birds of Nepal. Third edition.
Kathmandu: Nature Himalayas.
Gurung, K. K. (1983) The heart of the jungle. The wildlife of Chitwan. London: Andre Deutsch and
Kathmandu: Tiger Tops.
Hurlbert, S. H., Loayza, W. and Moreno, T. (1986) Fish-flamingo-plankton interactions in the
Peruvian Andes. Limnology and Oceanography 31: 457-468.
Inskipp, C. (1988) A birdwatchers’ guide to Nepal. Sandy: Prion.
Inskipp, C. (1989) Nepal’s forest birds; their status and conservation. Cambridge, U.K.: International
Council for Bird Preservation Monograph No. 4.
Inskipp, C. and Inskipp, T. (1991) A guide to the birds of Nepal. Second edition. London: Christopher
Helm.
King, B., Dickinson, E. C. and Woodcock, M. (1975) H field guide to the birds of South-East Asia. London:
Collins.
Ormerod, S. J. (1990) Riverine birds and land use in Nepal. Oriental Bird Club Bulletin 11: 13-17.
Ormerod, S. J. and Tyler, S. J. (1 986) Biometrics, growth and sex ratios amongst Welsh Dippers Cinclus
cinclus. Ringing & Migration 7: 61-70.
Ormerod, S. J. and Tyler, S. J. (1987) Dippers Cinclus cinclus and Grey Wagtails Motacilla cinerea as
indicators of stream acidity in upland Wales. Pp. ? in A. W. Diamond and F. Filion, eds., The value
of birds. Cambridge, U.K.: International Council for Bird Preservation.
Ormerod, S. J. and Tyler, S. J. (1988) Some aspects of foraging ecology of Green Sandpipers Tringa
ochropus. Bird Study 35: 25-30.
Rand, A. L. and Fleming, R. L. (1957) Birds ofNepal. Fieldiana: Zoo!. 41: 1-218.
Ripley, S. D. (1950) Birds from Nepal 1947-49. J. Bombay Nat. Hist. Soc. 49: 355-417.
Schoener, T. W. ( 1 982) The controversy over interspecific competition. American Scientist 70: 585-595.
C* „1 _ \V7 A Thp CPYllfll ?12£ Himnmhum of South German Dinners (Cinclus
82
DR. S. J. TYLER and DR. S J. ORMEROD
Forktail 9
APPENDIX 1
DESCRIPTION OF THE LIKHU KHOLA AND TRIBUTARIES
Dee Khola - open, very few alders, little riparian vegetation - either grazed, cut or cultivated to edge; some steep rocky
dry hillsides with stunted scrub/tree growth; side tributaries with narrow strip of alder carr. Many irrigation channels
diverting water from stream and much sandy sediment on stream bed. Large boulders in stream, but only two or three
small (1 m high) waterfalls. South-facing.
Mahadev Khola - similar to Dee but riparian vegetation in patches by wooded sections and narrow gorge with cliffs and
waterfalls up to 4 m high, for 300-400 m. Lower section with many rocks and stones. Wetted area reduced to trickle
through irrigation diversions; much sediment and very turbid water. Hillside erosion in upper reaches. Channel width
in low’er section c. 10-15 m but stream reduced to 5-8 m. Gorge only 6-8 m wide. South-facing.
Bore Khola - narrow stream mainly with steep banks with shrubs and trees overhanging much of stream; and adjacent
Sal forest in patches. Elsewhere rice fields. Rocks and boulders abundant but no true waterfalls. Many irrigation channels
and much sediment on stream bed. Highest section more open. North-facing.
Svalping - broadest (20 m) of tributaries surveyed with good flow. Steep banks, many with fringe of trees and shrubs; some
waterfalls; numerous rocks and boulders. North-facing.
Ghvambe Khola - a tributary of the Svalping - through woodland for much of survey stretch; meandering and rocky,
narrow 4-6 m. More open in upper stretch.
Bhondare and Togi - two narrow subtributaries, 2-8 m in width; the lower part of the Jogi through cultivation; little
bankside cover; series of high rocky waterfalls at upper end of stretch surveyed; the Bhondare through cultivation too but
in a narrow rocky channel with thick vegetation on streamsides; cliffs and waterfalls; a small trickle only in upper section
Likhu Khola - Upper 2 km surveyed rocky, open fast-flowing, 20-40 m wide; mainly I m depth; many shoals, riffles, some
deep pools with riverside cliffs. Little riparian vegetation except odd patches and degraded forest along one bank for 500
m below the Syalping confluence. Alluvial terraces cultivated up to river edge. Much disturbance by local people and
stock. Two bridges across the river and easily fordable elsewhere.
Lower section in broad open valley, extensive shoals and river much braided, channel up to 500 m across. Gradient
reduced cf. upper section.
1994
FORKTAIL 9 (1993): 83 - 88
83
Winter records of the Manchurian
Reed- Warbler Acrocephalus ( agricola )
tangorum from Thailand
PHILIP D. ROUND
Non-breeding season records of the Manchurian Reed-Warbler Acrocephalus ( agricola ) tangorum are
reported from Thailand. These are the only observations of this taxon away from north-east China and
Amurland, Russia where it both breeds and has been recorded on passage. A. tangorum shows some
distinct differences from nominate A. a. agricola and its taxonomic and conservation status should be
examined anew, particularly as it may be severely threatened by habitat destruction in its Thai winter
quarters.
INTRODUCTION
The Manchurian Reed-Warbler Acrocephalus ( agricola ) tangorum is a little
known taxon which breeds in in both Heilongjiang province and the Nei
Mongkol Autonomous Region in north-east China (Cheng 1 987, Alstrom et
al. 1991) and in Russian Amurland (Shibnev and Gluschenko 1977, Stepanjan
1978, Gluschenko 1989). It has also been recorded on passage, in the
western part of Chaoyang, Liaoning Province (Cheng 1987) and at
Qinhuangdao, Hebei Province from which it was first described (La Touche
1912). Kennerley and Leader (1992), Williams et al. (1992) and Williams
and Hsu (1992) have recently detailed a number of sightings of migrant
tangorum at the nearby sites of Beidaihe and Daihe in both spring and
autumn.
This paper documents the first records of tangorum away from north-east
Asia, in its presumed winter quarters in Thailand.
THE FIND
The author, together with Dr Boonsong Lekagul, was netting migrant
passerines in a freshwater marsh at Khao Sam Roi Yot, Prachuap Khiri Khan
Province, south-western Thailand (1 2°1 0’N 99°54’E) on 6 May 1981, when
he noticed an unusually rufous warbler with only a slight blackish brow
among a number of Black-browed Reed-Warblers A. bistrigiceps trapped.
This was immediately recognised as being similar to a skin labelled/!, agricola
which the author had previously examined at the Centre for Thai Reference
Collections, Thailand Institute of Scientific and Technological Research,
Bangkok. That specimen (number 53-2875), a first autumn female, had
84
P. D. ROUND
Forktail 9
been collected by Dr J. T. Marshall at Bang Phra Red Cross Horse Farm,
Chon Buri Province, south-eastern Thailand (13°11’N 100°59’E) on 9
October 1967. The Khao Sam Roi Yot bird (Field number ACW 14) was
collected for deposition at the Centre for Thai National Reference Collections.
The presence of a slight, but noticeable, black brow in both specimens
indicated, according to Vaurie (1959), that the birds might be A. ( agricola )
tangorum and this was confirmed when the Khao Sam Roi Yot skin was
compared with a series of eleven specimens of tangorum held at the British
Museum (Natural History) in August 1982.
Subsequent observations of tangorum at Khao Sam Roi Yot were sight
records of single birds by the author, Ben King and a Kang Bird tour group
on 1 7 January 1 985, and by the author and J. Dunn on 1 5 February 1985.
A number of other sightings of tangorum at Khao Sam Roi Yot have been
reported in subsequent years up to the present.
One further tangorum was netted in a marsh at Rangsit, Pathum Thani
Province, on the northern outskirts of Bangkok (13°59’N 100°38’E) by
Kevin Baker on 3 March 1 987. After examination, it was photographed and
released.
These appear to be the only records of this taxon away from north-east
Asia.
DESCRIPTION
The two Thai specimens of tangorum showed fresh to slightly worn body
plumage, having warm rufescent-brown upperparts, with the rufous tinge
being strongest on the rump and upper tail coverts, and rufous-edged tertials.
The crowns of both birds appeared slightly mottled, the individual feathers
having blackish-brown centres and olive-brown edges. The blackish feather
centres were particularly prominent on the lateral crown, above the supercilium,
forming a slight blackish brow which extended from the anterior margin to
just behind the hind margin of the eye. The broad, buffy supercilium
extended from the base of the bill to roughly half way between the rear margin
of the eye and the nape. There was a blackish-brown line through the eye.
The throat was clear white while the breast, flanks and under tail coverts
were a bright rufous tawny-buff. On the specimen examined live by the
author, the maxilla was blackish-grey and the lower mandible entirely pale
flesh. The legs were flesh-coloured and the iris muddy-brown. The label of
the Bang Phra specimen gave the iris colour as grey.
The upperparts of the October specimen were slightly paler and more
evenly rufescent than those of the May (Khao Sam Roi Yot) bird and the
rectrices showed slight to moderate wear. On the May bird, the rufescent tint
on the upperparts was somewhat reduced, particularly on the upper back, as
1994
Winter records of the Manchurian Reed-Warbler from Thailand
85
Table 1. Biometrics and wing formula of Thai specimens of Acrocephalus ( agricola ) tangorum
(Lengths given in mm). Primaries are numbered descendantly. Under column p9, - 4
mm (=4/5) indicates that the tip of the 9th (second outermost) primary falls 4 mm short
of the wing point, and lies between the tips of 4th and 5th primaries.
the rufescent tips and edges of the body feathers had begun to abrade,
revealing the darker feather centres. In contrast, the rectrices of the May bird
were fresher with darker centres and deeper more intensely rufous edges than
those of the October specimen and had been recently moulted, together with
all three tertials on both wings. The innermost secondary on the left wing had
also been renewed but the primaries and all remaining secondaries were
unmoulted and the primaries, in particular, showed moderate to heavy wear.
Both specimens were similar in plumage colouration to a series of seven
skins collected by J. D. D. La Touche in August and September 1912 and
September 1913 from Qinhuangdao, Hebei Province, North-east China,
held at BMNH. Four further skins at BMNH, collected at the same locality
during 30 May to 2 June 1913, differed markedly in being more worn, and
are duller and greyer, appearing olive-brown above, and whiter on the
underparts. Although Williamson (1968) surmised that tangorum probably
underwent a complete moult in its winter quarters, the Khao Sam Roi Yot
bird, though it had renewed body and coverts feathers, tertials and tail, had
clearly not moulted most remiges suggesting that a partial moult on the
wintering grounds, rather than a complete moult, may be the norm. Although
the body plumage may perhaps be expected to wear or bleach, losing its
markedly rufescent tint over most of the upperparts and underpans, somewhat
paralleling the seasonal change in hue of nominate A. agricola , all rectrices of
86
P. D. ROUND
Forktail 9
the four spring tangonim at BMNH appeared so heavily worn that they could
not have been moulted as recently as those of the Khao Sam Roi Y ot bird and
had either not been moulted since the previous year, perhaps while still on
the breeding grounds (if adult) or perhaps not moulted at all (for birds in their
first calendar year) . Photographs of two spring individuals in Kennerley and
Leader (1992) showed similar, heavily worn rectrices. The Khao Sam Roi
Yot bird, therefore, may have undergone an uncharacteristically extensive
partial moult. The third bird, from Rangsit in March, had not yet undergone
any pre-breeding moult and the overall colouration appeared closer to that
of A. bistrigiceps,, being only slightly more rufous on the upperparts (K. Baker
in litt. 1993). Some biometrics and wing formula data for all three birds are
given in Table 1 .
STATUS AND HABITAT IN THAILAND
All but two of the Thai records come from a single locality, Khao Sam Roi
Yot, the site of possibly the largest remaining Phragmites swamp in Thailand,
covering roughly 50 sq km. The marsh is fringed with some Typha
angustifolia Linn, together with other lower growth (probably Eleocharis dulcis
(Burm.f.) Trin. ex Hensch.. and Scirpus mucronatus Linn.) around its drier
margins. Rangsit is a Typha marsh of less than 1 sq km area. Bang Phra is
a water storage reservoir in relatively dry country which, at the time of capture
of the tangorum specimen (October, in the late wet-season) would probably
have supported a number of shallow flooded areas around its margins. The
bird was said to have been caught in a grass field (Pantuwatana et al. 1969).
Notwithstanding the potential difficulty in separating tangonim in the field
from the commoner and more widespread Blunt-winged Warbler A concinens,
or from the similarly scarce and local nominate race of the Paddyfield
Warbler A. a. agricola (so far known only from two specimens from marshy
areas in the far north of the country (King 1966, Round 1983) and a few
probable sight records) it is surprising that more tangonim have not yet been
recorded, especially considering the large number of birdwatchers visiting
Thailand. This may indicate its genuine scarcity: ten A. bistrigiceps were
trapped to only one tangonim at Khao Sam Roi Yot during 4-6 May 1991.
The combination of sight records in January and February, and the specimen
in May strongly suggests that tangonim winters at Khao Sam Roi Yot,
whereas the Bang Phra bird, taken in October, seems more likely to have been
on migration. (The author mist-netted Acrocephalus warblers at Bang Phra
in September and December 1982 without locating any tangonim). The
situation at Rangsit is unclear but it is indeed surprising that there are no sight
records of tangonim from there, since it is one of the most heavily watched
sites anywhere in the lowlands of Thailand. As far as we know, therefore,
1994
Winter records of the Manchurian Reed-Warbler from Thailand
87
tangorum may be mainly or entirely restricted to Khao Sam Roi Yot in winter
though it is possible that increased mist-netting could unearth further birds
in other areas.
THE CONSERVATION AND STATUS OF A. (a.) tangorum
Notwithstanding the inherent difficulty of separating smaller Acrocephalus
warblers, tangorum appears to be genuinely scarce in its winter quarters.
Furthermore, its only known wintering site, in the reedswamp at Khao Sam
Roi Yot National Park, Thailand, has been very adversely affected by
drainage and conversion to shrimp and fish ponds since 1986 (Parr et al.
1993), leading the IUCN Commission on National Parks and Protected
Areas to list the site as one of the most threatened parks in the world. Khao
Sam Roi Yot is probably the last major reedswamp in Thailand. Elsewhere,
such minor freshwater swamps as remain, around the margins of major
rice-growing areas, especially within a 150 km radius of Bangkok, are
dominated by Typha and lack any expanses of Phragmites : all are imminently
threatened by reclamation and urbanisation. Other than at Khao Sam Roi
Yot, no freshwater swamp habitat has ever been incorporated within the
boundary of any national park or wildlife sanctuary in Thailand.
The taxonomic position of tangorum still needs further clarification.
Alstrom et al. ( 1991) clearly demonstrated that Williamson’s (1968) placement
of tangorum as a race of the Black-browed Reed-Warbler A. bistrigiceps - an
arrangement subsequently followed by Watson et al. (1986) - was spurious.
Although they continued to treat tangorum as a subspecies of A. agncola, as
previously considered by Vaurie (1 959), on the basis of its territorial response
to song playback from nominate A. agricola , this was never tested by playback
of any other Acrocephalus as a control and may therefore be inconclusive.
Indeed, Alstrom and Olsson (1992) subsequently suggested that a positive
response to playbacks may be of little or no taxonomic value because of
known instances where taxa have responded to the songs of both close
congeners and even unrelated species.
A. tangorum has a significantly larger bill then nominate agricola and, in
addition, in worn plumage shows consistently darker, browner upperparts
(Alstrom et al. 1991, Kennerley and Leader 1992). These slight but
consistent differences and the large range-gap between the breeding ranges
of the two might still suggest that tangorum is better treated as a distinct
species which, especially in view of its probable threatened status, deserves
renewed attention. A. tangorum is already considered rare or threatened in
Gluschenko (1989) who recommended measures to prevent its reedbed
breeding habitat from burning or reclamation for agriculture. Further efforts
should be made to determine its precise distribution and the size of breeding
88
P. D. ROUND
Forktail 9
populations from singing males. Pressure should also be placed upon the
Thai government to ratify the RAMSAR convention, demarcate and protect
the boundary of Khao Sam Roi Yot National Park as well as to create or
rehabilitate reedswamps elsewhere in central Thailand.
I thank the staff of the Sub-department of Ornithology, British Museum (Natural History) for access to
specimens and, in particular, Peter Colston for his generous assistance. I am grateful to Kevin Baker
for providing details of the langorum netted at Rangsit, and to Per Alstrdm and Peter Kennerley for
commenting on a draft of this paper. M. G. Wilson helpfully translated from the Russian references.
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most threatened parks. Otyx 27: 245-249.
Round, P. D. (1983) Some recent bird records from northern Thailand. Nat. Hist. Bull. Siam Soc. 31:
109-122.
Shibnev, U. B. and Gluschenko, U. N. (1977) [‘Two new species of reed warblers in the fauna of the
Soviet Union’] . Abstracts of VII All-Union Ornithology Conference, part 1 , Kiev. p. 113. (In Russian.)
Stepanjan, L. S. (1978) Sostav i raspredelente ptits faulty SSR. Passeriformes. Moskow.
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in E. Mayr and G. W. Cottrell, eds., Check-list of birds of the world, 1 1 . Cambridge, Massachusetts:
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Williams, M. D., Carey, G. J., Duff, D. G. and Xu Weishu (1992) Autumn bird migration at Beidaihe,
China, 1986-1990. Forktail 7: 3-55.
Williams, M. D. and Hsu, W. S. (1992) Birds at Beidaihe, late spring 1991. China Flyway 2: 1 1-14.
Williamson, K. (1968) Identification for ringers 1: the genera Cettia, Locustella, Acrocephalus and
Hippolais. Third edition. Tring: British Trust for Ornithology.
Philip D. Round, Center for Conservation Biology, Faculty of Science, Mahidol University, Rama 6 Road,
Bangkok 10400, Thailand.
1904
FORKTAIL 9 (1993): 89 - 119
89
Birds recorded during the third
BirdLife/Forest Birds Working Group
expedition in Viet Nam
C. R. ROBSON, J. C. EAMES, NGUYEN CU and
TRUONG VAN LA
Between 1 2 April and 5 July 1991, surveys of forest birds were undertaken at a selection of sites, including
protected areas, in Viet Nam. These surveys were part of the Viet Nam Forest Project of BirdLife
International and provided information on the status and distribution of 1 6 globally threatened and 1 3
near-threatened species (Collar and Andrew 1988) and other endemic species. Information was
obtained on Orange-necked Partridge Arborophila davidi , Green Peafowl Pavo muticus , White-winged
Duck Cairma scutulata. Pale-capped Pigeon Columba punicea, White-shouldered Ibis Pseudibis davisoni
and Black-hooded Laughingthrush Gamdax milled. In addition, an undescribed taxon offulvetta/l/ap/>(>
was discovered on Mount Bi Doup near Da Lat, Lam Dong Province (South Annam).
Between 1 2 April and 5 July 1 99 1 surveys for globally threatened and other
endemic forest birds were undertaken at a selection of sites in Viet Nam.
These surveys formed part of the Viet Nam Forest Project of BirdLife
International and the Forest Birds Working Group of the Centre for Natural
Resources Management and Environmental Studies (CRES) and the Institute
of Ecology and Biological Resources, Hanoi.
The main aims of this fieldwork were to undertake surveys for four globally
threatened endemic species; Orange-necked Partridge, Edwards’s Pheasant
Lophura edwardsi, Black-hooded Laughingthrush Gamdax milled and Grey-
crowned Crocias Crocias langbianis and to identify core areas for their
protection. Other objectives were to undertake further surveys for White¬
winged Duck Cairina scutulata and Green Peafowl Pavo muticus in Nam Bai
Cat Tien National Park and to conduct more detailed faunal surveys at Cong
Troi and other remaining forest areas on the Da Lat Plateau. For a full
account of the results of these surveys, including the implications for
conservation, see Eames et al. (1992).
During fieldwork, new distributional data were obtained on Vietnamese
birds and are presented in this paper. Of particular note was the discovery
of Orange-necked Partridge Arborophila davidi and White-shouldered Ibis
Pseudibis davisoni in Nam Bai Cat Tien N.P. Information was obtained on
the status of 14 other globally threatened species, namely Siamese Fireback
Lophura diardi, Germain’s Peacock-Pheasant Polyplectron germaini, Crested
Argus Rheinardia ocellata, Green Peafowl, White-winged Duck, Blyth’s
Kingfisher Alcedo hercules , Pale-capped Pigeon Columba punicea , Chinese
Egret Egretta eulophotes, Lesser Adjutant Leptopdlos javanicus. Bar-bellied
Pitta Pitta elliodi , Y ellow-billed Nuthatch Sitta solangiae, Short-tailed Scimitar-
90
C. R. ROBSON etal.
Forktail 9
Babbler Jabouilleia danjoui, Black-hooded Laughingthrush and Collared
Laughingthrush Garrulax yersini, and 13 near-threatened species: Red-
vented Barbet Megalaima lagrandieri, Coral-billed Ground-Cuckoo
Carpococcyx renauldi. Yellow-vented Green-Pigeon Treron seimundi, Roseate
Tern Sterna dougallii, Pied Falconet Microhierax melanoleucus, Malayan
Night-Heron Gorsachius melanolophus, Schrenck’s Bittern Ixobrychus
eurhythmus, White-winged Magpie Urocissa whiteheadi, Ratchet-tailed Treepie
Temnurus temnurus , Green Cochoa Cochoa viridis. White-cheeked
Laughingthrush Garrulax vassali, Spot-breasted Laughingthrush G. merulinus
and Grey-faced Tit-Babbler Macronous kelleyi (Collar and Andrew 1988).
ORNITHOLOGICAL REGIONS OF VIET NAM
As in our previous papers (Robson et al. 1989, 1993) we follow the sub¬
divisions of Annam proposed by King et al. ( 1 97 5) and the division of T onkin
into East and West proposed by Vo Quy (1983). The region ‘Indochina’,
referred to in this paper, comprises of Laos, Viet Nam and Cambodia
collectively.
ABBREVIATIONS
c. = circa, FIPI = Forest Inventory and Planning Institute, Ministry of
Forestry, Hanoi, ha = hectares, km = kilometres (in a direct line), mm =
millimetres, m = metres above sea level, N.P. = national park.
ITINERARY
1994
Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
91
N
A
102°
a
ZOOGEOGRAPHICAl REGIONS:
A WEST TONKIN
B EAST TONKIN
C NORTH ANNAM
D CENTRAL ANNAM
E SOUTH ANNAM
F COCHINCHINA
TOWNS & CITIES
O | SURVEY LOCALITIES
1 Mount Bi Doup
2 Long Lanh
3 Long Lanh East
4 Cong Troi South
5 Cong Troi North
6 Mount Lang Bian
7 Tuyen Lam
8 Klong
9 Da Dung
1 0 Da Lat area
11 Di Linh Village '8'
12 Mount Pantar
13 Deo Nui San
14 Nam Bai Cat Tien NP
15 Bach Ma NP
16 Nam Dong District
17 Tram Chim Reserve
18 Dong Nai Delta
19 Phan Thiet salt pans
20 Cam Ranh Bay
21 Lake Cau Hai
' _ ’’Y ,
A
^Quy Nhon
Nha Trang
12°-
\ 19^
Saigon,
(Ho Chi Minh City)
Figure 1. Viet Nam, showing locations mentioned in text.
92
C. R. ROBSON etal.
Forktail 9
MAIN LOCALITIES VISITED
/. Mount Bi Doup ( 12'05’N 108°40,E)
Mount Bi Doup (2,289 m) is the highest peak on the Da Lat Plateau, situated
to the north-east of Da Lat, Lam Dong Province (South Annam).
The vegetation on the mountain is similar to that on Mount Lang Bian
(Robson et al. 1993). However, the area of Tropical Montane Evergreen
forest (MacKinnon and MacKinnon 1986) here is much larger (at least
8,680 ha; Eames etal. 1992) and there are more extensive and mature stands
of pine. Additionally, due to the higher elevation of this mountain, there are
more rhododendrons and more extensive patches of bamboo in the
undergrowth. As on Mount Lang Bian, the lower slopes are largely
deforested or dominated by pine forest with pockets of degraded evergreen
forest. Some open slopes are covered with bracken and grass.
The forest here has been classified as a special protection area by the Lam
Dong Forest Department, which means that, officially, no logging or other
forms of forest exploitation are allowed. There appeared to be relatively little
disturbance to forest on the mountain, although some areas had recently
been burnt on the lower slopes.
2. Long Lanh (2°08’N 1081°39’E)
This site includes the village of that name and surrounding area, situated to
the north-west of Mount Bi Doup.
The vegetation here is considerably modified, consisting of large open
areas of grassland in a broad river valley, with patches of pine Pinus insularis
forest, relatively mature in places. The terrain is fairly level (1,450-1 ,500 m).
3. Long Lanh East (12"09’N 108"41’E)
Situated immediately north of Mount Bi Doup and east north-east of Long
Lanh.
The vegetation consists entirely of Tropical Montane Evergreen forest
(MacKinnon and MacKinnon 1 986) and covers an area of 5,346 ha (Eames
et al. 1992), forming a contiguous block with evergreen forest on Mount Bi
Doup. Elevation varies from 1,500-1,800 m. Some areas had recently been
cleared for agriculture; old, disused clearings are overgrown with dense scrub
and secondary growth. A recently constructed logging track runs through the
area.
This forest has been classified as a watershed protection area by the Lam
Dong Forest Department, which means that only selective logging is
permitted. Small scale operations were being carried out, specifically to
extract large specimens of Fokienia hodginsii.
1994
Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
93
4. Cong Troi South (12°06’N 108°23’E)
This site is at and below a pass (1,800 m) situated 18 km north north-west
of Da Lat, Lam Dong Province (South Annam).
The vegetation consists entirely of Tropical Montane Evergreen forest
(MacKinnon and MacKinnon 1986) and elevation ranges from 1,500-1,800
m.
5. Cong Troi North (12°09’N 108°23’E)
Situated 20-25 km north north-west of Da Lat, Lam Dong Province (South
Annam).
The vegetation here is the same as at the previous site, at an elevation of
around 1 ,500 m. There are some clearings for agriculture and areas of open
grassland. An unpaved road runs through the area.
6. Mount Lang Bian (12°02’N, 108°26’E)
This site, situated to the north of Da Lat, Lam Dong Province (South
Annam) was described in detail by Robson et al. (1993).
Clearance of evergreen forest for charcoal production was continuing at an
alarming rate.
7. Tuyen Lam (11°52’N 10825' E)
Ho Tuyen Lam is a reservoir 6 km south south-west of Da Lat, Lam Dong
Province (South Annam).
The reservoir is immediately surrounded by pine forest, behind which are
relatively extensive areas of T ropical Montane Evergreen forest (MacKinnon
and MacKinnon 1986). Elevation varies from 1,400-1,500 m.
Small scale unofficial logging was being carried out in a number of areas
and parts of the forest backing the reservoir shore were being cleared for
agriculture.
8. Klong (11°49’N 108"28’E)
A small roadside settlement below a forested hillside, 1 4 km south of Da Lat,
Lam Dong Province (South Annam).
Vegetation here consists of a little degraded pine forest, scrub and
cultivation on the lower slopes and Tropical Montane Evergreen forest
(MacKinnon and MacKinnon 1986) above 1,350 m. Elevation, during the
survey, varied from 1,050-1,400 m.
Much of the forest was heavily cut-about and there was evidence of hunting
in the area.
94
C. R. ROBSON etal.
Forktail 9
9. Da Dung (11°59’N !08rl9’E).
North-west of Da Lat, Lam Dong Province (South Annam).
1 0. Da Lat area (Da Lat ; 11°57’N 108527’ E).
Lam Dong Province (South Annam).
11. DiLinh village ‘8’ (11'42’N 10800’ E).
Lam Dong Province (South Annam).
12. Mount Pantar (11°29’N 108 06’ E )
A forested mountain (Nui Pantar, 1 ,664 m) situated 1 1 km south of Di Linh,
Lam Dong Province (South Annam).
The vegetation here consists of patches of pine forest and scrub on the
lower slopes and Tropical Montane Evergreen forest (MacKinnon and
MacKinnon 1986) above 1 , 1 00 m. Elevation, during the survey, varied from
1,080-1,350 m.
Much of the evergreen forest had been cut-about or consisted of secondary
growth. Some quite large areas were being cleared for cultivation on the
lower slopes.
13. Deo Nui San (11°28’N 108 04’ E)
A forested pass between Mount San (1,502 m) and Mount Pantar, 13 km
south of Di Linh, Lam Dong Province (South Annam).
The vegetation here consists entirely of Tropical Montane Evergreen
forest (MacKinnon and MacKinnon 1986), with elevation ranging from
1,160-1,220 m.
The north side of the pass is threatened by clearance of forest for
agriculture.
14. Nam Bai Cat Tien National Park (11°27’N 107°18,E)
This site, situated in the northern part of DongNai Province (Cochinchina)
was described in detail by Robson et al. (1993).
15. Bach Ma National Park (16°11’N 107° 50’ E)
Situated between Hue and Da Nang in Thua Thien Province (Central
Annam), this site was also described in detail by Robson et al. (1993).
However, in 1991 we also visited the southern part of the park, basing
1994
Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
95
ourselves in the Khe Ao Valley mouth (16°08’N 107°48’E).
Vegetation in the Khe Ao area consists of Lowland Evergreen forest
(MacKinnon and MacKinnon 1986), also described as Closed Broadleaved
Ombrophilous Lowland (CVRER 1985) and Lowland Semi-Evergreen
forest (MacKinnon and MacKinnon 1986) or Closed Broadleaved Tropical
Evergreen Seasonal Lowland dominated by Dipterocarpaceae, Fabaceae,
Meliaceae and Sapindaceae (CVRER 1985). A broad river valley runs east
to west through the area but was cleared of its forest by herbicide spraying
during the Viet Nam War; consequently there is only scrub and grass
remaining in the more level areas. Elevation, during the survey, varied from
130-400 m.
The watershed to the south-east of Khe Ao has been proposed as a
southerly extension to the park. Collection of rattans for export was posing
a serious threat here and in other parts of the national park.
16. Nam Dong District (16°10’N 107°38’E).
Situated to the west of Bach Ma NP, Thua Thien Province (Central Annam) .
17. Tram Chim Reserve (10°45’N 105°35,E).
Dong Thap Province (Cochinchina).
18. Dong Nai Delta (Duyert Hai; 10°25’N 106°58’E).
Thanh Pho Ho Chi Minh Province (Cochinchina).
19. Phan Thiet salt pans (10°57’N 108°07’E).
Thuan Hai Province (South Annam).
20. Cam Ranh Bay (ll°5rN 109°07,E).
Khanh Hoa Province (South Annam).
21. Lake Cau Hai (16°20’N 107°48,E).
Thua Thien Province (Central Annam).
22. On route in Cochinchina.
23. On route in South Annam.
24. On route in Central Annam.
96
C. R. ROBSON etal.
Forktail 9
RECORDS OF PARTICULAR INTEREST
RAIN QUAIL Cotumix coromandelica A male in excellent condition was
found for sale in a shop in Da Lat (1,500 m) on 28 May. It had been trapped
in nearby fields in February 1991.
This appears to be the first record of the species from Viet Nam and
Indochina. A series of colour photographs were taken of the bird.
ORANGE-NECKED PARTRIDGE Arborophila davidi Two birds were
observed briefly by C.R.R. in Nam Bai Cat Tien N.P. (140-200 m) on 21
June. Seven days were subsequently spent in search of these birds but they
were only seen again in flight by C.R.R. and N.C. on 22 and 24 June.
The habitat consisted of non-thorny bamboo forest, very dense in places
and reaching a height of c. 6-10 m, on small hills (Eames et al. 1992), with
light undergrowth including various gingers Zingiberaceae. Scaly-breasted
Partridge A. chloropus was commonly heard calling in surrounding areas of
level lowland forest but never on hills, indicating different habitat preferences.
Orange-necked Partridge shows similarities with the more widespread Bar-
backed Partridge A brunneopectus and appears to replace it geographically in
Cochinchina.
It was previously known only from two specimens collected at 250 m near
Bu Kroai (Bu Croi), Song Be Province (Cochinchina) by M. A. David-
Beaulieu in 1927. Delacour and Jabouille (1931), erroneously state that
there were three specimens and that two of them were lost. It was listed as
globally threatened by Collar and Andrew ( 1 988) . Bu Kroai is 37 km north¬
west of the above mentioned sightings.
EDWARDS’S PHEASANT Lophura edwardsi Surveys were undertaken to
locate this species in Quang Tri and Thua Thien Provinces (Central
Annam), including Bach Ma N.P. No evidence of its continued existence
could be found. For a full account see Eames et al. (1992).
SIAMESE FIREBACK Lophura diardi Small numbers were recorded along
the main track through Nam Bai Cat Tien N.P. (140 m) on a number of
occasions.
As elsewhere in its range, it becomes habituated to road and track-sides
through forest. It was considered globally threatened by Collar and Andrew
(1988).
GERMAIN’S PEACOCK-PHEASANT Polyplectron germaini Reliably
reported to occur at Tuyen Lam (1,400-1,500 m) by local wood-cutters on
28 May. The remains of a snared bird were examined in Da Longit village,
on the Da Dung River, 10-15 km north-west of Da Lat, Lam Dong Province
(South Annam) on 1 June. It had been caught three or four hours walk
downstream of the village. The full tail of a bird shown to us by a local hunter
at Di Linh Village ‘8’ (Ta Lung; 1 1°44’N 108ll01’E; 610 m), on the upper
1994
Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
97
Dong Nai River, north-west of Di Linh, Lam Dong Province (South Annam)
on 5 June, had been killed in low hills to the north. A male was seen and three
others heard on Mount Pantar (1,080-1,100 m) on 6 June. Recorded almost
daily in Nam Bai Cat Tien N.P. (140 m) where it was considered to be fairly
common; for more details see Eames etal. (1992) and Robson etal. (1993).
Recorded in montane evergreen forest on Mount Pantar. It was considered
globally threatened by Collar and Andrew (1988).
CRESTED ARGUS Rheinardia ocellata At least 21-26 birds were heard
calling in the southern part of Bach Ma N.P., including its proposed southern
extension (200-700 m), between 27 April and 1 May (Eames etal. 1992) and
several birds were heard in the north-east of the park where they were
surveyed in 1990 (Robson etal. 1993). One bird was heard in the Ba Long
Valley (300-400 m), 30 km south-west of Quang Tri, Quang Tn Province
(Central Annam) on 5 May. Reported by local people from Nam Dong
District (200-300 m) on 8 May and a number of sites in the hills south-west
of Hue, Thua Thien Province and south-west of Quang Tri, Quang Tri
Province (Central Annam) during 3-6 May (Eames etal. 1992). Three birds
were heard calling on Mount Bi Doup (1,700-1,900 m) on 22 and 23 May
and two were heard calling at nearby Long Lanh East (1,700 m) on 24 May.
The records from Mount Bi Doup and Long Lanh East are to the south of
its previously recorded range in Viet Nam (Eames et al. 1992) and the first
from the Da Lat Plateau. However, Brunei (1978) had previously reported
seeing feathers of this species in the Da Lat area. Interestingly, it was found
at a much higher elevation in these areas than those previously surveyed by
us to the north (Robson etal. 1989, 1993). It was listed as globally threatened
by Collar and Andrew (1988).
GREEN PEAFOWL Pavo muticus Reported by local people to still occur
in the Ba Long Valley area, 30 km south-west of Quang Tri, Quang Tri
Province (Central Annam) on 5 May. A 1989 sighting of two birds was
reported by a local hunter at Di Linh Village ‘8’ (Ta Lung; 11°44’N
108°01 ’E; 610 m), on the upper Dong Nai River, north-west of Di Linh, Lam
Dong Province (South Annam) on 5 June. At least eleven birds were
observed at various localities in Nam Bai Cat Tien N.P. during 9-26 June
(Eames et al. 1992).
It was difficult to survey at the latter locality, as territorial calling was not
noted and birds were moulting (Eames et al. 1992). According to reports
from local tribes in Central Annam, most populations of this species
disappeared between the late 1950s and 1975 and mostly between 1968 and
1975, coinciding with the defoliation of river valleys during the Viet Nam
War. The species is globally threatened (Collar and Andrew 1988).
WHITE- WINGED DUCK Cairina scutulata None was observed during
surveys carried out in Nam Bai Cat Tien N.P. However, local people reliably
98
C. R. ROBSON etal.
Forktail 9
reported that two birds had been present in the north-east of the park earlier
in the year (Eames et al. 1992).
It was considered globally threatened by Collar and Andrew (1988).
SPOT-BILLED DUCK Anas poecilorhyncha At least 80 adults and three
broods of small young at the Tram Chim Reserve on 16 April.
Not recorded by King et al. (1975) and Vo Quy ( 1 983) from Cochinchina.
WHITE-BELLIED WOODPECKER Dryocopus javensis Two birds were
seen in pine forest at Long Lanh (1,450 m) on 24 May.
King et al. (1975) record it only above 915 m in north-east Burma and
north-west Tonkin, Viet Nam.
RED-VENTED BARBET Megalaima lagrandieri Fairly common in the
southern part of Bach Ma N.P. (130-400 m) on 28-29 April; several heard
in Nam Dong District (200-300 m) on 8 May; several birds heard calling at
Klong (1,350 m) on 18 May; at least two calling at Tuyen Lam (1,450 m) on
28 May; one heard in the Di Linh Village ‘8’ area (930 m) on 5 June; many
birds heard calling on Mount Pantar (1,080-1,350 m) on 6 June; common
at Deo Nui San (1,1 60- 1 ,220 m) on 7 June; fairly common in Nam Bai Cat
Tien N.P. (140 m).
Widespread in Viet Nam, with an elevation range of 50-1,900 m (Robson
etal. 1989, 1993) but listed as near-threatened by Collar and Andrew (1988).
BANDED KINGFISHER Lacedo pulchella One male seen and another
heard in the southern part of Bach Ma N.P. (130-300 m) on 28 April.
Not recorded for Central Annam by King et al. (1975) or for northern
Annam by Vo Quy (1983). However, Delacour and Jabouille (1931)
mention Thua Luu, just north-east of Bach Ma N.P., as a locality for the
species.
BLYTH’S KINGFISHER Alcedo Hercules One seen in the Khe Thuong
Valley (150 m), in the proposed southerly extension of Bach Ma N.P. on 30
April (Eames et al. 1992).
In Viet Nam this species was said to occur only in Tonkin by King et al.
(1975) and Vo Quy (1983). However, Stepanyan et al. (1983) give a record
from Kon Ha Nung, Gia Lai Kon Turn Province (Central Annam) and we
found it in North Annam in 1990 (Robson et al. 1993). It was considered
globally threatened by Collar and Andrew (1988).
CRESTED KINGFISHER Megaceryle lugubris One at Ho Vang (1,450 m),
just north of Da Lat, Lam Dong Province (South Annam) on 30 May.
Not recorded for South Annam by King et al. (1975) or Vo Quy (1983).
CORAL-BILLED GROUND-CUCKOO Carpococcyx renauldi Several
heard calling in the north-east part of Bach Ma N.P. (400 m) on 26 April.
Considered near-threatened by Collar and Andrew (1988).
1994
Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
99
SILVER-BACKED NEEDLETAIL Hirundapus cochinchinensis At least 40
birds in the southern part of Bach Ma N.P. on 27-28 April and two in Nam
Dong District on 8 May.
Not recorded for Central Annam by King et al. (1975) or for northern
Annam by Vo Quy (1983).
BROWN-BACKED N E E D LET A I L /Trim dap us giga nteus Fairly common
in Bach Ma N.P. during 20-28 April.
Not listed for Central Annam by King et al. ( 1 975), or for northern Annam
by Vo Quy (1983). We recorded it in North Annam for the first time in 1988
(Robson et al. 1989).
FORK-TAILED SWIFT Apus pacificus In Bach Ma N.P., at least ten birds
on 23 April and one on 30 April. At least three birds at Mai Lanh, Quang
Tri Province (Central Annam) on 5 May.
Not recorded for Central Annam by Delacour and Jabouille (1931). King
et al. (1975) list the species as a resident in Central Annam but do not include
South Annam, an area mentioned by the former authors.
HOUSE SWIFT Apus nipalensis Seen flying around the summit of Mount
Lang Bian (2,167 m) on 31 May.
Not previously recorded above 1,830 m in South-East Asia (King et al.
1975).
: EASTERN GRASS-OWL Tyto longimembris A feather of this species was
found in grassland at Long Lanh (1,450 m) on 21 May and subsequently
identified by comparison with specimens in the British Museum, Tring.
Several mounted specimens examined in Da Lat (1,500 m) in May were said
to have been shot nearby. Not previously recorded above 1 ,220 m in South-
East Asia (King et al. 1975).
SPOT-BELLIED EAGLE-OWL Bubo nipalensis A mounted specimen was
.examined in a shop in Da Lat on 29 May. The shopkeeper said it had come
from Buon Me Thuot, Dac Lac Province (South Annam).
King etal. (1975) and Delacour and Jabouille (1931) do not list it for South
Annam.
PALE-CAPPED PIGEON Columba punicea At least 14 birds at Da Dung
(1,280 m) on 1 June and eight to ten there the following day (Eames et al.
1992).
The birds were found feeding on fruiting trees with large numbers of
parakeets, bulbuls and starlings in an area of overgrown cultivation. It was
considered globally threatened by Collar and Andrew ( 1 988) . Not previously
recorded above 1,220 m in South-East Asia (King et al. 1975).
YELLOW- VENTED GREEN-PIGEON Treron seimundi One seen on
Mount Pantar (1,350 m) on 6 June and several birds at nearby Deo Nui San
(1,160 m) on 7 June.
It was considered near-threatened by Collar and Andrew (1988).
100
C. R. ROBSON eial.
Forktail 9
SARUS CRANE Grits antigone Up to 120 birds, including a flock of 70-80,
at the Tram Chim Reserve on 16 April.
BLACK-TAILED GODWIT Limosa limosa Two on salt pans by the south¬
west corner of Cam Ranh Bay on 12 May.
Not recorded for South Annam by King et al. (1975) or Vo Quy (1983).
BAR-TAILED GODWIT Limosa lapponica Three on salt pans by the south¬
west corner of Cam Ranh Bay on 12 May.
Not recorded for South Annam by King et al. (1975) or Vo Quy (1983).
TEREK SANDPIPER Tringa cinerea On salt pans by the south-west corner
of Cam Ranh Bay, one on 18 April and at least 30 on 12 May.
Not recorded for South Annam by King et al. (1975) or Vo Quy (1983).
RUDDY TURNSTONE Arenaria interpres One at Duyen Hai, Dong Nai
Delta on 14 May.
Not recorded for Cochinchina by King et al. (1975) or Vo Quy (1983).
SHARP-TAILED SANDPIPER Calidris acuminata One on Phan Thiet salt
pans on 18 April.
King et al. (1975) do not list Viet Nam in the range of this species, and it
is not mentioned in Vo Quy (1 983). However, Fischer (1961, 1974, 1983)
mentioned its occurrence in East Tonkin.
RED-NECKED PHALAROPE Phalaropus lobatus On salt pans by the
south-west shore of Cam Ranh Bay, at least 4 1 on 1 8 April and 1 4 on 12 May.
Two by the causeway at Lang Co, Thua Thien Province (Central Annam)
on 20 April.
There is one previous record for Viet Nam and Indochina in the unpublished
notes of Nils Gyldenstolpe (Eames and Ericson in prep.); a female shot in a
small clay-pit full of water at Lao Bao, Quang T ri Province (Central Annam)
on 19 October 1938.
PHEASANT-TAILED JACANA Hydrophasianus chirurgus Two birds were
seen flying north over the forested hills of Bach Ma N.P. on 1 May.
King et al. (1975) list this species as a resident throughout Indochina but
Delacour (1929) stated that northern breeders move south in winter.
ORIENTAL PLOVER Charadrius veredus One on Phan Thiet salt pans on
12 May.
The only previous Vietnamese record was from Da Nang in Central
Annam (Delacour and Jabouille 1931).
HERRING GULL Larus argentatus One second-summer bird at Thuan An,
Thua Thien Province (Central Annam) on 22 April.
Although listed as a coastal migrant throughout Indochina by King et al.
(1975), no previous records for Central Annam could be found in available
literature. The bird was believed to be L. a. vegae , a race that is treated as
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Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
101
a separate species by Glutz and Bauer (1982). Previous Vietnamese records
of Herring Gull from East T onkin, North Annam and Cochinchina were also
thought to be of this subspecies (Delacour 1929, Delacour and Jabouille
1931). Fischer (1961, 1965) thought that his records in East Tonkin possibly
related to Yellow-legged Gull L. cachinnans mongolicus.
BRIDLED TERN Sterna anaethetus Up to 1 20 birds off the municipal beach
at Qui Nhon, Binh Dinh Province (Central Annam) on 10 May and at least
three off Nha Trang, Khanh Hoa Province (South Annam) on 1 1 May.
Previously recorded only from the Con Son Islands (Cochinchina) in Viet
Nam (King et al. 1975).
ROSEATE TERN Sterna dougallii Several birds seen off the municipal
beach at Qui Nhon, Binh Dinh Province (Central Annam) on 9 May.
Not definitely recorded for Viet Nam or Indochina by King et al. (1975)
and not listed for Viet Nam by Delacour and Jabouille (1931) or Vo Quy
(1983). However, it was listed for the Con Son Islands by Robinson and
Kloss (1921), based on Sparrman’s (1789) description of Lams Polo-candor.
However, Sparrman’s description, although clearly relating to a Sterna tern,
is not referable to S', dougallii (T. Inskipp pers. comm. 1993).
COMMON TERN Sterna hirundo Several seen off the municipal beach at
Qui Nhon, Binh Dinh Province (Central Annam) on 9 May.
Not definitely recorded for Viet Nam or Indochina by King et al. (1975)
and not listed for Viet Nam by Delacour and Jabouille (1931) or Vo Quy
(1983). There has, however, been a recent sighting in East Tonkin (Scott et
al. 1989).
LITTLE TERN Sterna albifrons In Khanh Hoa Province (South Annam):
two between Van Ninh and Co Ma on 1 9 April, at least three off Nha Trang
on 1 1 May, four at Ca Na on 12 May and eight to ten on salt pans by the
south-west corner of Cam Ranh Bay on 12 May. Two on Phan Thiet salt
pans on 12 May.
Not recorded for South Annam by King et al. (1975) or Vo Quy (1983).
One nest with three eggs was found on a salt pan bund at Cam Ranh Bay.
WHITE-WINGED TERN Chlidonias leucopterus Seven birds at Thanh
Binh, Dong Thap Province (Cochinchina) on 16 April; at least 75 feeding
over marshes south of Hoa Vinh, Phu Yen Province (South/Central Annam)
on 10 May; 28 moving north past Nha Trang, Khanh Hoa Province (South
Annam) on 1 0 May with another 50 past on 1 1 May; at least 1 80 birds at Nin
Hai, Thuan Hai Province (South Annam) on 12 May; eight at Phan Rang,
Thuan Hai Province (South Annam) on 1 2 May; two at Nha Be, Thanh Pho,
Ho Chi Minh Province (Cochinchina) on 14 May.
Not recorded for Cochinchina and South Annam by King et al. (1975) or
Vo Quy (1983).
102
C. R. ROBSON etal.
Forktail 9
GREY-HEADED FISH-EAGLE Ichthyophaga ichthyaetus One bird seen in
the southern part of Bach Ma N.P. on 27 April and at least four birds in Nam
Bai Cat Tien N.P. during 1 1-13 June.
Considered a lowland forest specialist by Round (1988).
CRESTED GOSHAWK Accipiter trivirgatus A single bird seen displaying
over the summit of Mount Bi Doup (2,289 m) on 23 May.
Not previously recorded above 1,830 m in South-East Asia (King et al.
1975).
PIED FALCONET Microhierax melanoleucus One seen in Nam Dong
District (200-300 m) on 8 May.
Not recorded for Central Annam by King et al. (1975). However,
Delacour and Jabouille (1931) mention a record from the Col des Nuages
(Hai Van Pass) in Central Annam. Our record is marginally the furthest
south for the species.
CHINESE EGRET Egretta eulophotes Eight birds, including seven in full
summer plumage, on inter-tidal mudflats in the south-west corner of Cam
Ranh Bay on 18 April (Eames et al. 1992).
This is the second record for Viet Nam and Indochina, the first being from
East Tonkin (Scott 1988). The species was considered globally threatened
by Collar and Andrew (1988).
PURPLE HERON Ardea purpurea A roost of at least 50 birds in Nam Bai
Cat Tien N.P. on 20 June.
MALAYAN NIGHT-HERON Gorsachius melanolophus A single bird was
flushed from the edge of a stream in Nam Bai Cat Tien N.P. on 13 June.
Considered a near-threatened species by Collar and Andrew (1988).
SCHRENCK’S BITTERN Ixobrychus eurhythmus One female seen near the
headquarters of Bach Ma N.P. on 25 April.
The only previous Vietnamese records were from T onkin (King etal. 1975,
Vo Quy 1983). It was listed as near-threatened by Collar and Andrew
(1988).
GREAT BITTERN Botaurus stellaris One mounted specimen was found for
sale in Da Te market, west Lam Dong Province (Cochinchina) on 8 June.
According to the shopkeeper it had been purchased earlier in the year from
a local hunter.
Not recorded for Cochinchina by King et al. (1975) or Vo Quy (1983).
WHITE-SHOULDERED IBIS Pseudibis davisoni Three birds were observed
calling and displaying in Nam Bai Cat Tien N.P. ( 1 40 m) on 1 3 and 1 4 June
and local people reported that six were present in the same area earlier in the
year (Eames et al. 1992).
This record constitutes the first sighting of wild birds in continental South-
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Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
103
East Asia for many years. It was considered globally threatened by Collar and
Andrew (1988)
PAINTED STORK Mycteria leucocephala A total of 18 birds at the Tram
Chim Reserve on 16 April.
WOOLLY-NECKED STORK Ciconia episcopus Five birds were seen in
Nam Bai Cat Tien N.P.
LESSER ADJUTANT Leptoptilos javanicus A single bird was flushed from
a pool in Nam Bai Cat Tien N.P. on 19 June.
Its reluctance to leave the area suggested that it may have been breeding
locally. This locality is currently the only known breeding site for the species
in Viet Nam (Morris 1988, Scott 1989). It was considered globally
threatened by Collar and Andrew (1988).
BAR-BELLIED PITTA Pitta elliotii Small numbers were recorded in the
southern part of Bach Ma N.P. and in Nam Bai Cat Tien N.P. Although it
was considered a globally threatened species by Collar and Andrew (1988),
it is now considered less threatened than was previously thought and may no
longer warrant its classification as globally threatened (Eames et al. 1992).
GOLDEN-BELLIED GERY GONE Gerygone sulphurea One bird seen and
two or three heard at the Tram Chim Reserve, on 16 April; several birds
singing by the south-west shore of Cam Ranh Bay on 18 April and 12 May;
common in mangrove forest between Nha Be and Duyen Hai, Thanh Pho
Ho Chi Minh Province (Cochinchina) on 14 May.
Not recorded for South Annam by King et al. (1975) or Vo Quy (1983).
The former authors refer to its occurrence in Viet Nam as being based on an
‘old breeding record’ from Cochinchina.
WHITE- WINGED MAGPIE Urocissa whiteheadi Heard calling in the
north-east of Bach Ma N.P. on 26 April.
Listed as near-threatened by Collar and Andrew (1988).
RATCHET-TAILED TREEPIE Temnurus temnurus Several observed in
the north-east and southern parts of Bach Ma N.P. on 26 and 28 April
respectively.
Listed as near-threatened by Collar and Andrew (1988).
EURASIAN BLACKBIRD Turdusmerula Two birds near the headquarters
of Bach Ma N.P. on 24-25 April.
Not recorded for Central Annam by King et al. (1975). However,
Delacour and Jabouille (1931) mention wintering records from Quang Tri,
Hai Lang and Hue in Central Annam. Our records appear to be the furthest
south in Viet Nam to date.
GREEN COCHOA Cochoa viridis One calling on Mount Lang Bian ( 1 ,900-
2,000 m) on 31 May was tape-recorded.
Considered near-threatened by Collar and Andrew (1988).
104
C. R. ROBSON era/.
Forktail 9
GREY-STREAKED FLY CATCHER Muscicapa griseisticta One in gardens
near the headquarters of Bach Ma N.P. on 24-26 April.
The only previous Vietnamese and Indochinese record was from
Cochinchina (Delacour and Jabouille 1931).
NARCISSUS FLYCATCHER Ficedula narcissina A female of the nominate
subspecies in gardens near the headquarters of Bach Ma N.P. on 23 April.
There are only two previous Vietnamese and Indochinese records of this
subspecies, from Quang Tri and Hue (Central Annam) in March and April
(Delacour and Jabouille 1931).
BLUE-THROATED FLY CATCHER Cyornis rubeculoides One male on 1 0
June and a pair on 18 June in Nam Bai Cat Tien N.P. (140 m).
Not recorded for Cochinchina by Kang et al. (1975) or Vo Quy (1983).
One of the males observed was atypical, lacking the usual orange coloration
on the breast. Instead, the lower throat/upper breast was white and the
remainder of the breast off-white with some darker blotching; reminiscent of
the atypical Hainan Blue-Flycatcher C. hainanus depicted in Boonsong and
Round (1991).
CHESTNUT-TAILED STARLING Stumus malabaricus A pair seen at the
nest at Long Lanh (1,450 m) on 21 May.
Not previously recorded above 1,220 m in South-East Asia (King et al.
1975). The nest was situated in a hole in a pine tree and contained young.
CHESTNUT-VENTED NUTHATCH Sitta nagaensis Recorded at 1 ,080
m on Mount Pantar on 6 June.
Not previously recorded below 1,370 m in South-East Asia (King et al.
1975).
YELLOW-BILLED NUTHATCH Sitta solangiae At least three birds at
Cong Troi North (1,510 m) on 17 and 30 May; several at Cong Troi South
(1,500-1,700 m) on 19 May; several on Mount Bi Doup (1,800-2,100 m) on
22-23 May; at least six at Long Lanh East (1,500-1,800 m) on 24 May; up
to ten at Tuyen Lam (1,450-1,500 m) on 27-28 May and at least four on
Mount Lang Bian (1,900 m) on 31 May (Eames et al. 1992).
In South Annam, we have only recorded this species between 1,450 and
2,100 m on the Da Lat Plateau (see Robson etal. 1993) and the closely related
Velvet-fronted Nuthatch V. frontalis between 930 m and 1,350 m on the
adjacent Di Linh Plateau and slopes leading up to the Da Lat Plateau (see
Robson et al. 1993). It was considered globally threatened by Collar and
Andrew (1988).
YELLOW-BROWED TIT Sylviparus modestus Seen at Tuyen Lam (1 ,500
m) on 27 May.
Not previously recorded below 1,830 m in South-East Asia (King et al.
1975).
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Birds recorded during the third Birdlife/Forest Birds expedition in Vie Nam
105
GREEN-BACKED TIT Pams monticolus Seen at Klong (1D50 m) on 18
May.
Not previously recorded below 1,525 m in South-East Asa (King et al.
1975).
NORTHERN HOUSE-MARTIN Delichon urbica At last one bird
amongst a flock of feeding hirundines at Mai Lanh, QuangTri Province
(Central Annam) on 5 May.
Not recorded for Central Annam by King et al. (1975) oi for northern
Annam by Vo Quy (1983). It was identified as this species nther than the
similar Asian House-Martin D. dasypus by its deeply forkedtail and pure
white underparts.
GREY-EYED BULBUL Iole propinqua Seen at Deo Nui Sar( 1,220 m) on
7 June.
Not previously recorded above 915 m in South-East Ask (King et al.
1975).
GOLDEN-HEADED CISTICOLA Cisticola exilis A male singing in the
southern part of Bach Ma N.P. on 27 April; at least three, incuding singing
males, at Ke Che (Khe Tche), just west of Bach Ma N.P. on 1 May; at least
two singing at Long Lanh (1,450 m) on 21 May; fairly common and
confirmed breeding in Nam Bai Cat Tien N.P.
Not recorded for Cochinchina by King etal. (1975) orVo Qiv (1983). The
records from Central Annam appear to extend its range norhward in Viet
Nam (see Robson et al. 1989). Not previously recorded abcre 1,220 m in
South-East Asia (King et al. 1975). It seems that this specieshas expanded
its range in Viet Nam as a result of deforestation.
PLAIN PRINIA Prinia inomata Several birds singing at Lon; Lanh (1,450
m) on 21-22 May.
Not previously recorded above 915 m in South-East Ask (King et al.
1975).
YELLOW-BELLIED PRINIA Prinia flaviventris Two or thre birds singing
at Long Lanh (1,450 m) on 21 May.
Not previously recorded above 1,220 m in South-East Asa (King et al.
1975).
PALE-FOOTED BUSH-WARBLER Cettia pallidipes Up ts four singing
males on the lower slopes of Mount Bi Doup (1,550 m), in suiable breeding
habitat, on 22-23 and 25 May.
These records constitute a remarkable breeding range extmsion for the
species, as King etal. (1975) and Vo Quy (1983) only record t as a migrant
to West Tonkin in Viet Nam (subspecies laurentei). One biri was trapped
and photographed and a full series of biometrics and notes wire taken. No
differences between these birds and C. p. laurentei could be fund during a
106
C. R. ROBSON etal.
Forktail 9
subsequent comparison of our material with skins in the British Museum,
Tring. A recording of the song was compared with a tape of song from north¬
west Thailand (subspecies laurentei) made by P. D. Round and it was found
to differ only slightly. The habitat consisted of open bracken-covered slopes.
ORIENTAL REED-WARELERHcrocep/zu/rr? orientalis Three or four birds
by the south-west shore of Cam Ranh Bay on 18 April.
Not recorded for South Annam by King et al. (1975) or Vo Quy (1983).
TWO-BARRED WARBLER Phylloscopus plumbeitarsus One seen in gardens
near the headquarters of Bach Ma N.P. on 24 and 26 April.
Not recorded for Central Annam by Delacour and Jabouille (1931).
YELLOW-BELLIED WARBLER Abroscopus superciliaris Small numbers
were recorded in Nam Bai Cat Tien N.P. during 16-22 June.
Not recorded for Cochinchina by King et al. (1975) or Vo Quy (1983).
BLACK-HOODED LAUGHINGTHRUSH Garrulax milleti A flock of at
least ten birds atCongTroi North (1,510 m) on 17 and 30 May with another
flock of at least five there on the latter date; two flocks of at least five and three
at Tuyen Lam (1,500 m) on 27 and 28 May respectively; a flock of at least
three birds seen and another one or two flocks heard on Mount Pantar
(1,100-1,350 m) on 6 June and a flock of at least eight seen and another two
or three flocks heard at Deo Nui San (1,160-1,220 m) on 7 June.
The first records of this Vietnamese endemic since it was reported by
Brunei 30 years previously (Brunei 1978). All the birds we saw were in flocks
in the undergrowth of broadleaved evergreen forest. The relatively low
altitudinal range of the species makes it particularly vulnerable to agricultural
encroachment (Eames et al. 1 992) and it was considered globally threatened
by Collar and Andrew (1988). Its vocalisations are very similar to the closely
related Grey Laughingthrush G. maesi and White-necked Laughingthrush
G. strepitans.
WHITE-CHEEKED LAUGHINGTHRUSH Garrulax vassali Three or
four at Klong (1,050-1,200 m) on 18 May; one at Cong Troi South (1,700
m) on 1 9 May; several birds including at least one juvenile at Long Lanh East
(1,500-1,700 m) on 24 May; at least 30 birds at Tuyen Lam (1,450-1,500
m) on 27-28 May; a flock of at least 35 birds at Cong Troi North (1,510 m)
on 30 May; several at Da Dung (1,280 m) on 1 June; several in the Di Linh
Village ‘8’ area (930 m) on 5 June; at least ten on Mount Pantar (1,080 m)
on 6 June and several at Deo Nui San (1,200 m) on 7 June.
To date, we have recorded this species from 650-1,900 m, in grass, scrub
or evergreen forest edge, often in large flocks (see Robson et al. 1989, 1 993) .
It was considered near-threatened by Collar and Andrew (1988).
SPOT-BREASTED LAUGHINGTHRUSH Garrulax merulinus Two
pairs seen and another male heard at Long Lanh East ( 1 ,500 m) on 25 May;
one male seen and another heard at Tuyen Lam (1,450 m) on 28 May; two
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Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
107
at Cong Troi North (1,510 m) on 30 May; several singing males on Mount
Pantar (1,100-1,350 m) on 6 June and three seen and three or four males
heard at Deo Nui San (1,160-1,220 m) on 7 June.
The subspecies involved, annamensis, is very distinctive and endemic to
the highlands of South Annam. Birds were found in undergrowth in cut-over
primary and secondary broadleaved evergreen forest, secondary growth
between abandoned cultivation and primary forest and at the edge of primary
and secondary forest. A male was trapped and photographed at Long Lanh
East. The species was considered near-threatened by Collar and Andrew
(1988).
COLLARED LAUGHINGTHRUSH Garrulax yersini At least eight birds
at Cong Troi South (1,500-1,700 m) on 19 May; several on Mount Bi Doup
(1,800-2,100 m) on 22-23 May; up to ten birds at Long Lanh East (1,500-
1,800 m) on 24-25 May; at least three at Cong Troi North (1,510 m) on 30
May and several on Mount Lang Bian (1,900 m) on 31 May.
To date, we have recorded the species between 1 ,500 m and 2,100 m. Two
birds were trapped and one photographed at Cong T roi South. It is endemic
to Viet Nam and was considered globally threatened by Collar and Andrew
(1988).
SHORT-TAILED SCIMITAR-BABBLER Jabouilleia danjoui Three seen
and another heard on Mount Bi Doup (1,980-2,000 m) on 22-23 May and
a family party of four birds at Long Lanh East (1,700 m) on 24 May (Eames
et al. 1992).
These records are apparently the first of the southern (nominate) subspecies
since its discovery in the 1920s (Delacour et al. 1928, Robinson and Kloss
1919). The southern subspecies appears to occur at higher elevations than
the northern subspecies (J. d. parvirostris ), which we have found only from
50-900 m (Robson et al. 1989, 1993). The species is endemic to Viet Nam
and was considered globally threatened by Collar and Andrew (1988).
GREY-FACED TIT-BABBLER Macronous kelleyi One singing in the
southern part of Bach Ma N.P. (130 m) on 29 April; two or three singing in
Nam Dong District (200-300 m) on 8 May; common in the Di Linh Village
‘8’ area (930 m) on 5 June; one or two singing on Mount Pantar (1,080 m)
on 6 June and fairly common in Nam Bai Cat Tien N.P. (140-250 m) during
9-25 June.
The records from Mount Pantar appear to be the highest to date (see
Robson etal. 1989, 1993). It was considered near-threatened by Collar and
Andrew (1988).
YELLOW-EYED BABBLER Chrysomma sinense One bird in Nam Bai Cat
Tien N.P. on 13 June.
Not previously recorded for Cochinchina by King et al. (1975) or Vo Quy
(1983).
108
C. R. ROBSON etal.
Forktail 9
CHESTNUT-FRONTED SHRIKE-BABBLER Pteruthius aenobarbus Seen
in the Di Linh Village ‘8’ area (930 m) on 5 June.
Not previously recorded below 1,220 m in South-East Asia (King et al.
1975).
FULVETTA Alcippe sp. On Mount Bi Doup (2, 1 60-2,289 m), one bird on
22 and 23 May and a flock of at least four on 23 May.
One bird was trapped and photographed in the hand and a full description
and series of biometrics were taken. After an analysis of specimens in the
British Museum, Tring and other material, we decided that these birds most
resemble A. mficapilla danisi. It appears that this subspecies is known only
from a single specimen (no. 268,092 in the Museum of Comparative
Zoology, Cambridge, U.S.A.) which was collected on Phu (Mount) Kobo
(2,000 m), northern Laos by Delacour and Greenway in 1938 (Delacour and
Greenway 1941). Cheng (1987) listed dam's?' from south-east Yunnan and
south-west Guizhou, China, noting that they were ‘originally identified asA
r. sordidior , but from zoogeographical viewpoint, the specimens collected
probably belong to A. r. danisi ’; the assignation of these specimens is perhaps
doubtful. Several differences were noted during a comparison of our material
with photographs of the danisi specimen held in the U.S.A.; notably the less
extensive area of silvery-whitish coloration visible at the base of the primaries
on the closed wing on the Bi Doup birds.
The habitat where birds were found on Mount Bi Doup consisted of
bamboo undergrowth in montane broadleaved evergreen forest and scrub in
a clearing on the summit.
More data are currently being gathered on the Bi Doup birds and it is hoped
that a full account will be published soon.
MOUNTAIN FULVETTA Alcippe peracensis To date, we have recorded/1.
p. groteiatihe. following localities (see Robson etal. 1989, 1993): Cue Phuong
N.P., Ha Nam Ninh Province (East Tonkin), Buon Luoi, Gia Lai Kon Turn
Province (Central Annam) and Son Tung, Nghe Tinh Province (North
Annam) in 1 988; throughout the lowland parts of Bach Ma N.P. in 1 990 and
1 99 1 and at Cat Bin, Nghe Tinh Province (North Annam) in 1 990; Nam Bai
Cat Tien N.P. in 1991. We recorded it from 50-700 m and breeding was
confirmed at Son Tung and Bach Ma N.P. A. p. annamensis was recorded
in the Pass ‘41’ area, A Sau A Luoi, Quang Tri/Thua Thien Province
(Central Annam) in 1988; Mount Bach Ma in Bach Ma N.P. in 1990 and
commonly at many localities on the Da Lat and Di Linh Plateaus, Lam Dong
Province (South Annam) during 1 990 and 1991. We recorded it from 700-
2, 1 00 m and breeding was confirmed on Mount Lang Bian. The subspecific
identification of birds observed at Kon Cha Rang (at 700-850 m), Gia Lai
Kon Turn Province (Central Annam) in 1988 remains undetermined.
We believe that the subspecies grotei has been wrongly assigned to
1994
Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
109
Mountain Fulvetta. Its biometrics, song and altitudinal range place it much
closer to Brown-cheeked Fulvetta A. poioicephala. Additionally, in 1 990, we
found grotei and annamensis occurring together in Bach Ma N.P.; the former
below 700 m and the latter above 900 m. Morphologically, grotei is distinct
from both Brown-cheeked and Mountain Fulvettas and may prove to be a full
species.
Further research is currently underway and it is hoped that a paper will be
published on the status of A. p. grotei in the near future.
ORIENTAL SKYLARK Alauda gulgula In South Annam: several birds at
Phan Thiet salt pans on 18 April; several between Phan Rang, Thuan Hai
Province and Cam Ranh Bay, Khanh Hoa Province on 18 April; several
between Nha T rang and Van Ninh, Khanh Hoa Province on 1 9 April and 1 1
May and several by the south-west shore of Cam Ranh Bay on 1 2 May.
Not recorded for South Annam by King et al. (1975).
STREAKED SPIDERHUNTER Arachnothera magna Single birds were
recorded in Nam Bai Cat Tien N.P. (140 m) on 15 and 19 June.
There are no previous records for Cochinchina according to King et al.
(1975) and Vo Quy (1983). The former authors also state that it occurs only
above 915 m in Viet Nam.
VIETNAMESE GREENFINCH Carduelis monguilloti Several birds seen at
Klong (1,050 m) on 18 May.
Not previously recorded below 1,220 m (King et al. 1975). A flock of ten
birds, including juveniles, was observed flycatching from a pine Pinus
insularis (catching airborne termites) at Da Lat on 16 May (Eames et al.
1992).
We would like to express our gratitude to Geo-Initiative ‘Projekt Tropischer Regenwald e.V’ and the A.
S. Butler Charitable Trust for their financial support, and the Oriental Bird Club for providing a grant
to cover expenses incurred by Nguyen Cu and Truong Van La.
We would like to thank the following people for their support and assistance during the planning stages
of the 1991 visit: Dr. A. Green, R. F. A. Grimmett, Dr. G. E. Morris, S. Usui and R. Wirth.
In Viet Nam we were, once again, assisted by many people, without whom fieldwork would not have been
possible. We would particularly like to thank the following people: Prof. Dr Vo Quy and Dr Le Dien
Due (CRES); Dr Dang Huy Huynh and Dr Nguyen Tien Ban at the Centre for Ecology and Biological
Resources, Hanoi; Dr Doan Canh (FIPI); Truong Quang Tam and Dr Tran Van Minh at the Centre
for Ecology, T. P. Ho Chi Minh; Le Van Chiem (director), Bay Sot, Phan Thanh Tong and all the staff
at Nam Bai Cat Tien N.P.; Dr Nguyen Dang Khoi and staff at the Ecology Institute, Da Lat; Huynh
Van Keo (director) and staff at Bach Ma N.P.
Particular thanks are due to the hard work and enthusiasm of our driver Minh, whose skills enabled us
to reach many destinations which would otherwise have been inaccessible.
C. R. Robson, 63 Stafford Street, Norwich NR2 3BD, U.K.
J. C. Eames, c/o BirdLife International, Wellbrook Court, Girton Road, Cambridge CB3 ON A, U.K.
Nguyen Cu and Truong Van La, Institute of Ecology and Biological Resources, NCSR, Hanot, Viet Nam.
C. R. ROBSON etal.
Forktail 9
110
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Fischer, W. (1961) Kleine Beitriige zur Vogelkunde Vietnams. Beitr. Vogelk. 7: 285-317.
Fischer, W. (1965) Neue Beitrage zur Vogelkunde Vietnams. Beitr. Vogelk. 10: 361-379.
Fischer, W. (1974) Vorlaufiger Abschlussbcricht uber Vogel-beobachtungen in Vietnam. Beitr. Vogelk.
20: 249-300.
Fischer, W. (1983) Ein Beitriig zum Vorkommen, Durchzug und zur Ubersommerung von Limikolen
(Charadriiformes) in Vietnam. Beitr. Vogelk. 29: 297-305.
Glutz von Blotzheim, U. N. and Bauer, K. M. (1982) Handbuch der Vogel Mirteleuropas, 8/1.
King, B. F., Dickinson, E. C. and Woodcock, M. W. (1975) A field guide to the birds of South-East Asia.
London: Collins.
MacKinnon, J. and MacKinnon, K. (1986) Review of the protected areas system in the Indo-Malayan realm.
Gland, Switzerland and London, U.K. : International Union for Conservation of Nature and Natural
Resources.
Morris, G. E. (1988) Recent sight records of birds at Nam Cat Tien. Garrulax 4: 11-13.
Robinson, FI. C. and Kloss, C. B. (1919) On birds from South Annam and Cochin China. Ibis (11)1:
392-453, 565-625.
Robinson, H. C. and Kloss, C. B. (1921) Some birds from Pulo Condor e.J. Nat. Hist. Soc. Siam 4: 85-
91.
Robson, C. R., Eames, J. C., Wolstencroft, J. A., Nguyen Cu and Truong Van La (1989) Recent records
of birds from Viet Nam. Forktail 5: 71-97.
Robson, C. R., Eames, J. C., Nguyen Cu and Truong Van La (1993) Further recent records of birds
from Viet Nam. Forktail 8: 25-52.
Round, P. D. (1988) Resident forest birds in Thailand: their status and conservation. Cambridge, U.K.:
International Council for Bird Preservation (Monogr. 2).
Scott, D. A. (1988) Bird observations in Vietnam: 7-2 1 March 1988. Appendix XII of Wetland projects
in Vietnam, report on a visit to the Red River and Mekong deltas during March 1988. Unpublished.
Scott, D. A. (1989 )A directory of Asian wetlands. Gland, Switzerland and Cambridge, U.K.: 1UCN, The
World Conservation Union.
Scott, D. A., Howes, J. and Le Dien Due (1989) Management recommendations for Xuan Thuy
Reserve, Red River Delta. Appendix III: birds recorded in Xuan Thuy District, Red River Delta, 10-
12 March 1988 & 17-31 March 1989. Asian Wetland Bureau.
Sparrman, A. (1789) Museum Carlsonianum, in quo novas et selectas aves, coloribus ad vivum brevique
descriptione illustratus suasu el sumtibus generosissimi possessoris exhibet A. Sparrman.
Vo Quy (1983) [A catalogue of the birds of Vietnam]. Pp. 12-43 in L. N. Medvedev, ed. [Fauna and
ecology of the animals of Vietnam.] Moskva: Nauka. (In Russian.)
1994
Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
1 1 1
APPENDIX
ALL THE 1991 EXPEDITION’S BIRD RECORDS FROM VIET
NAM
The numbers following each species correspond to the places listed in the ‘main localities visited’ section at the beginning
of this paper.
The codes (in parentheses) which are attached to locality codes represent die following details of breeding and occurrence:
( ) Identification uncertain
[ ] Reported by local people
{ | Specimen, remains or feathers examined
B Breeding data obtained
C Adult observed carrying food
F Fledged young observed
M Birds observed carrying nest material
N Nest found:
e. With eggs
b. Nest building
i. Adult on nest
n. No contents
u. Contents unknown
y. With young
Chinese Francolin Francolinus piniadeanus
Rain Quail Commix coromandelica
Blue-breasted Quail C. chinensis
Rufous-throated Partridge Arborophila rufogularis
Bar-backed Partridge A. brwineopectus
Orange-necked Partridge A. davidi
Scaly-breasted Partridge A. chloropus
Ann am Partridge A (chloropus) merlini
Red Junglefowl Gallus gallus
Silver Pheasant Lophura nycihemera
Siamese Fireback L. diardi
Germain’s Peacock-Pheasant Polyplectron gcrmaim
Grey Peacock-Pheasant P. bicalcaratum
Crested Argus Rheinardia ocellata
Green Peafowl Pavo muticus
Lesser Whistling Duck Dendrocygna javanica
White-winged Duck Cairina scutulata
Cotton Pygmy-goose Nettapus coromandeliatius
Spot-billed Duck Anas poecilorhyncha
Garganey A. querquedula
Barred Buttonquail Tumix suscitator
Speckled Piculet Picumnus innominatus
White-browed Piculet Sasia ochracea
Grey-capped Woodpecker Dcndrocopos canicapillus
Rufous Woodpecker Celeus brachyurus
White-bellied Woodpecker Dryocopus javetisis
Lesser Yellownape Picus chlorolophus
Greater Yellownape P. Jlavinucha
Laced Woodpecker P. vittatus
Grey-faced Woodpecker P. canus
1.2.10.12.24
10
14
1,3,4,5,6,7,12
7,8,9,11,12,13,15
14
1.7
15
9(BF),14(BF),15,23,{24J
1,4, 6, 7, 11, 12, 15, [24]
14
[7], 19, 111, 12, 14
[24]
1.3.15.24
[11], 14, [24]
10.14.17.21.22.23.24
[14]
14
17(BP)
21
1.2.4.11.12.14.15.16.24
3,8(BF),9,12
14
1.2.6.10.12.14
1.7.14
2.14
7.14
1.2.4.7.9.11.14.15.16
14.15.16
2.7
112
C. R. ROBSON etal.
Forktail 9
Greater Flameback Chrysocolaptes lucidtis
Pale-headed Woodpecker Gecinulus grantia
Bay Woodpecker Blythipicus pyrrhotis
Black-and-buff Woodpecker Meiglyptes jugularis
Heart-spotted Woodpecker Hemicircus canente
Great Slaty W'oodpecker Mulknpicus pulverulentus
Red-vented Barbet Megalairna lagrandieri
Lineated Barbet At. lineata
Green-eared Barbet At. faiostricta
Golden-throated Barbet At. franklinii
Black-browed Barbet At. oorti
Moustached Barbet M. incognita
Blue-eared Barbet M. australis
Coppersmith Barbet At. haemacephala
Oriental Pied-Hornbill Anthracoceros albirostris
Great Hornbill Buceros bicomis
Wreathed Hornbill Aceros undulatus
Eurasian Hoopoe Upupa epops
O range- breasted Trogon Harpactes orcskios
Red-headed Trogon H. erythrocephalus
Indian Roller Coracias benghalensis
Dollarbird Eurystomus orientalis
Blyth’s Kingfisher Alcedo Hercules
Common Kingfisher A. atxhis
Blue-eared Kingfisher A. metiinting
Black-backed Kingfisher Ceyx erithacus
Banded Kingfisher Lacedo pulchella
Stork-billed Kingfisher Pelargopsis capensis
White-throated Kingfisher Halcyon smymensis
Black-cappf.d Kingfisher H. pileata
Collared Kingfisher Todirhamphus chloris
Crested Kingfisher Ategaceryle lugubris
Pied Kingfisher Ceryle rudis
Blue-bearded Bee-eater Nyctyomis aihertoni
Little Green Bee-eater Merops orientalis
Blue-throated Bee-eater At. viridis
Blue-tailf.d Bee-eater At. philippinus
Chestnut-headed Bee-eater At. leschenaulti
Chestnut-winged Cuckoo Clamator coromandus
Indian Cuckoo Cuculus micropterus
Banded Bay Cuckoo Cacomantis sonneratii
Plaintive Cuckoo C. merulinus
Asian Emerald Cuckoo Chrysococcyx maculatus
Violet Cuckoo C. xanthorhynchus
Drongo Cuckoo Sumiculus lugubris
Asian Koel Eudynamys scolopacea
Green-billed Malkoha Phaenicophaeus tristis
Coral-billed Ground-Cuckoo Carpococcyx renauldi
Greater Coucal Centropus sinensis
Lesser Coucal C. bengalensis
Vernal Hanging-Parrot Loriculus vcmalis
Grey-headed Parakeet Psittacula finschii
Blossom-headed Parakftt P. roseata
Red-breasted Parakeet P. alexandri
CRESTED Treeswift Hemiprocne coronata
1.14
14
1.4.6.7.8.12.13
14
14
14
7.8.11.12.13.14.15.16
14
14.15.16
12
1.4.5.11.15
1.3.5.7.8.9.11.13
14
22
14(BF)
12(BF), 13,14, 124|
14
23
14
3.7.8.11.13.14.16
14,23
1.2.9.14.15.16
15
15.17.19.21
14
14
14.15
14.15
9.1 1.12.14.15.16.23.24
15.24
18.21
10.15
14.17.21.23
4.11.12.13.14
1 1.14.17.23.24
15
23.24
14.15
15
4.15.16.24
7.11.14
14.15.16.17.21.22.23
15
14
5.6.14.15.16
23.24
7.11.12.13.14.15.16.24
15
2.8.9.10.11.14.15.16.23
2.9.1 1.13.14 (BF), 15,16,24
11.12.13.14.15.16
9,1 1
15
2.14
23
1994
Birds recorded during the third Birdiife/Forest Birds expedition in Viet Nam
113
Himalayan SvnFrLET Collocalia brevirostris
Germain’s SwiFrLET C. germani
Silver-backed Needletail Hirundapus cochinchinensis
Brown-backed Needletail H. gigameus
Asian Palm-Swift Cypsiums balasiensis
Fork-tailed Swift Apus pacificus
House Swift A. nipalensis
Eastern Grass-Owl Tyto longimembris
Mountain Scops-Owl Otus spilocephalus
Collared Scops-Owl O. lempiji
Spot-bellied Eagle-Owl Bubo nipalensis
Brown Fish-Owl Kerupa zeylonensis
Tawny Fish-Owl K. flavipes
Collared Owlet Glaucidium brodiei
Asian Barred Owlet G. cuculoides
Brown Hawk-Owl Ninox scutulata
Great Eared-Nightjar Eurastopodus macrotis
Grey Nightjar Caprimulgus indicus
Large-tailed Nightjar C. macnmts
Rock Pigeon Coluniba livia
Pale-capped Pigeon C. punicea
Spo tted Dove Streptopelia chinensis
Red Collared-Dove .S. tranquebarica
Barred Cuckoo-Dove Macropygia unchall
Emerald Dove Chalcophaps indica
Pink-necked Green-Pigeon Treron venians
Orange-breasted Green-Pigeon T. bicincta
Thick-billed Green-Pigeon T. curvirostra
Yellow-vented Green-Pigf.on T. seimundi
Wedge-tailed Green-Pigeon T. sphenura
Green-Pigeon Treron sp.
Green Imperial Pigeon Dticula aenea
Mountain Imperial Pigeon D. badia
Sarus Crane Grits antigone
Red-legged Crake Rallina fasciata
Si-aty-breasted Rail Gallirallus striatus
White-breasted Waterhen Amauromis phoenicurus
Ruddy-breasted Crake Porzana fusca
Watercock Gallicrex cinerea
Purple Swamphen Porphyria porphyrio
Common Moorhen Gallinula chloropus
Pintail Snipe Gallinago stenura
Black-tailed Godwit Limosa lirnosa
Bar-tailed Godwit L. lapponica
Whimbrel Numenius phaeopus
Eurasian Curlew N. arquata
Common Redshank Tringa totanus
Marsh Sandpiper T. stagnatilis
Common Greenshank T. nebularia
Wood Sandpiper T. glareola
T erek Sandpiper T. cinerea
Common Sandpiper T. hypoleucos
Grey-tailed Tattler T. brevipes
Ruddy Turnstone Arenaria interprcs
Rufous-necked Stint Calidris ruficollis
3
15.22.23.24
14.15.16
15
1 1,15,21,23
15.24
4,6,8, 1 0(BN), 1 5,22,23,24
2,110!
15
14.15.24
110!
14
14
3.4.5.12.13.15
8.14.15
14
14
2,10
14
10.16.23.24
9
2. 7. 9. 10. 12. 14. 15. 16. 21.22. 23. 24
15,17,23,24(BC)
1.2.3.9.11.12.14.15
11.12.13.14.15
14
15.24
11.16
12,13
8
14
14
1.3.4.11.12.13.15
17
14
15
10,14,15,16
14.15
14.21.22
14.17.23
10.15
15,21
20
20
18,20
18,20
18.19.20.23
17.19.20.23
17.18.19.20.21.22.23
17.21.23.24
20
15.17.19.20.21.23.24
20,23
18.19.20.24
18.19.20.23.24
1 14
C. R. ROBSON eta!.
Forktail 9
Temminck’s Stint C. temminckii
Long-toed Stint C. subminuta
Sharp-tailed Sandpiper C. acuminata
Curlew Sandpiper C. ferruginea
Broad-billed Sandpiper Limicola falcinellus
Red-necked Phalarope Phalaropus lobatus
Pheasant-tailed Jacana Hydrophasianus chinirgus
Bronze-winged Jacana Metopidius indicus
Black-winged Stilt Himantopus himantopus
Pacific Golden Plover Pluvialis fulva
Grey Pi over P. squatarola
Little Ringed Plover Charadrius dubius
Kentish Plover C. alexandrinus
Mongolian Plover C. mongolus
Greater Sand Plover C. leschenaultii
Oriental Plover C. veredus
River Lapwing Vanellus duvaucelii
Red-wattled Lapwing V. indicus
Oriental Pratincole Glareola maldivarum
Herring Gull Lams argemaius
Gull-billed Tern Sterna nilotica
Caspian Tern S. caspia
Roseate Tern S. dougallii
Black-naped Tern .S', stimatrana
Common Tern .S', hirundo
Little Tern S. albifrons
Bridled Tern S. anaethetus
Whiskered Tern Chlidonias hybridus
White-winged Tern C. leucopterus
Osprey Pandion haliaetus
Jerdon’s Baza Aviceda jerdoni
Black Baza A. leuphotes
Oriental Honey-Buzzard Penns ptilorhyncus
Black-winged Kite Elanus caeruleus
Brahminy Kite Haliastur indus
White-bellied Fish-Eagle Haliaeetus leucogaster
Grey-headed Fish-Eagle Ichthyophaga ichthyaetus
Crested Serpent-Eagle Spilomis cheela
Eastern Marsh-Harrier Circus spilonotus
Crested Goshawk Accipiter trivirgatus
Shikra A. badius
Besra A. virgatus
Black Eagle Ictinaetus malayensis
Rufous-belued Eagle Hieraeetus kienerii
Changeable Hawk-Eagle Spizaetus cirrhatus
Collared Falconet Microhierax caemlescens
Pied Falconet M. melanoleucus
Oriental Hobby Falco severus
Little Grebe Tachybaptus ruficollis
Oriental Darter Anhinga melanogastcr
Little Cormorant Phalacrocorax ntger
Little Egre t Egreua garzetta
Chinese Egret E. euhphotes
Pacific Reef-Egret E. sacra
Grey Heron Ardea cinerea
19
19.20
19
18.19.20
19
20.24
15.17
14.17
17.18.19.20
17,18,19,23
18.20
17.24
18.19.20.23.24
18.19.20.23.24
19.20.23.24
19
24
9,10,14,17,23,24(BN)
17.21.22.23.24
24
18
18
24
23.24
24
18,1 9,20(Bne),23,24
23.24
14.18.21.22.23.24
22.23.24
7.14.18.24
6
14.15
11.12.14.15
2.9.14.17.23.24
14,22
23
14.15
1,2,4,7,8,14,15,16
17
1.3.4.13.15
5.7.14
5
1(BF), 3, 4,5,6, 7, 8, 13, 16, 24
1,3
3,(?6)
14
16
10.14
7.10.17
14.17
7.14.17
14.15.18.21.23.24
20
18,20
17.18.19.20.23.24
1994
Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
115
Purple Heron A. purpurea
Great Egret Casmerodius albus
Intermediate Egret Mesoplioyx intermedia
Cattle Egret Bubulcus ibis
Chinese Pond-Heron Ardcola bacchus
Javan Pond-Heron A. spedosa
Striated Heron Buiorides striaius
Malayan Night-Heron Gorsachius melanolophus
Yellow Bittern Ixobrychus sinensis
Schrenck’s Bittern I. eurhythmus
Cinnamon Bittern I. cinnamomeus
Black Bittern I. flavicollis
Great Bittern Botaurus slellaris
White-shouldered Ibis Pseudibis davisoni
Painted Stork Mycteria leucocephala
Woolly-necked Stork Ciconia episcopus
Lesser Adjutant Leptoptilos javanicus
Blue-rumped Pitta Pitta soror
Rusty-naped Pitta P. oatesi
Blue Pitta P. cyanea
Bar-bellied Pitta P. elliotii
Blue-winged Pitta P. moluccensis
Dusky Broadbill Corydon sumatranus
Black-and-red Broadbill Cymbirhynchus macrorhynchos
Banded Broadbill Eurylaimus javanicus
Silver-breasted Broadbill Serilophus lunatus
Long-tailed Broadbill Psarisomus dalhousiae
Golden-bellied Gerygone Gerygone sulphurea
Grey-headed Canary-Flycatcher Culicicapa ceylotiensis
Asian Fairy-bluebird Irena puella
Blue-winged Leafbird Chloropsis cochinchinensis
Golden-fronted Leafbird C. aurifrons
Orange-bellied Leafbird C. hardwickii
Brown Shrike Lanius cristatus
Burmese Shrike L. collurioides
Long-tailed Shrike L. schach
Eurasian Jay Garrulus glandarius
White-winged Magpie Urocissa whiteheadi
Green Magpie Cissa chinensis
Yellow-breasted Magpie C. (thalassina) hypoleuca
Racket-tailed Treepie Crypsirina temia
Ratchet-tailed Treepie Temnurus temnurus
Black-billed Magpie Pica pica
Large-billed Crow Corvus macrorhynchos
Ashy Wood-swallow Ariamus fuscus
Slender-billed Oriole Oriolus tenuirostris
Black-hooded Oriole O. xanthomus
Maroon Oriole O. traillii
Large Cuckoo-shrike Coracina macei
Indochinese Cuckoo-shrike C. polioptera
Black-winged Cuckoo-shrike C. melaschisros
Grey-chinned Minivet Pericrocotus Solaris
Long-tailed Minivet P. ethologus
Scarlet Minivet P. flammeus
Bar-winged Flycatcher-shrike Hemipus picatus
14,17,21,23
14.17.20.23.24
15.17.23.24
15.23.24
10.15.16.21.23.24
17,18,22
15.18.20.21
14
14.15.21
15
10.14.15.16.21.23.24
14,15
{22|
14
17
14
14
14
110!
1.7.8.11.13
14.15
14
14
14(BN)
14
(13)
4.8.1 1 (BF), 1 2,15
17,18,20
1.3.4.5.6.7.8.9.11.12.13.15
8.9.11.12.13.14.15.16
11.14.15.16
14
15
15,17,21,22,23
1,2(BF),7(BF),9, 10(BF)
15.16.24
2.4.9.10
15
I, 3,6
4,13,14(BF)
I I, 14(BF),15,23,24
15
24
11.16.20.23.24
1.2.20.23.24
2,9
14
1.3.4.7.11
1.2.3.4.9.11.12.13.14.15
2,9,12
14.16
3.5.7.8.12.13
1.4.6.7.9.10
8.11.12.14.15
3,7,8,12,14
116
C. R. ROBSON etal.
Forktail 9
White-throated Fantail Rhipidura albicollis
Pied Fantail R. javanica
Black Drongo Dicrums macrocercus
Ashy Drongo D. leucophaeus
Bronzed Drongo D. aeneus
Lesser Racket-tailed Drongo D. remi/er
Hair-crested Drongo D. hottentotius
Greater Racket-tailed Drongo D. paradiscus
Black-naped Monarch Hyporhymis azurea
Asian Paradise-Flycatcher Terpsiphone parodist
Common Iora Aegithina tiphia
Great Iora A. lafrcsnayei
Large Woodshrike Tephrodornis gularis
Blue Rock-T brush Monticola solitarius
Blue Whistling-Thrush Myiophonus caeruleus
Orange-headed Thrush Zooihcra citrina
Dark-sided Thrush Z. marginata
Japanese Thrush Turdus cardis
Eurasian Blackbird T. merula
Lesser Shortwing Brachypieryx lencophrys
Grey-streaked Flycatcher Muscicapa griseisticta
Aslan Brown Flycatcher M. dauurica
Narcissus Flycatcher Ficcdula narcissina
Rufous-gorgeted Flycatcher F. strophiaia
Red-breasted Flycatcher /•'. parva
Rufous-browed Flycatcher F. soliians
Snowy-browed Flycatcher F. hyperyihra
Little Pied Flycatcher F. westermanni
Verditer Flycatcher Eumyias thalassina
Large Niltava Niltava grandis
Blue-throated Flycatcher Cyornis rubeculoides
Tickell’s Blue-Flycatcher C. tickelliae
Siberian Blue Robin Luscinia cyane
Oriental Magpie-Robin Copsychus saularis
White-rumped Shama C. malabaricus
White-tailed Robin Cinclidium leucurum
Slaty-backed Forktail Enicurus schistaceus
Spotted Forktail E. maculatus
Green Cochoa Cochoa viridis
Siberian Stonechat Saxicola maura
Pied Bushchat S. caprata
Grey Bushchat S. ferrea
Chestnut-tailed Starling Stumus malabaricus
White-shouldered Starling 5. sinensis
Black-collared Starling S. nigricollis
Vinous-breasted Starling S. burmannicus
Common Myna Acridotheres irisiis
Crested Myna A. crisiatellus
Golden-crested Myna Ampdiceps coronatus
Hill Myna Gracula religiosa
Chestnut-vented Nuthatch Sirra nagaensis
Velvet-fronted Nuthatch S. frontalis
Yellow-billed Nuthatch S. solangiae
Brown-throated T ree-creeper Ccrthia discolor
1.3.4.5.6.7.8.9.11.12.13
17,18
15.17.23.24
I, 2(BF),4,6(BF),7,8,9,10,1 1,12,13, 1 4(BF),
15(Bny), 16
I I, 13,14(BF),1 5,16
1.3.4.5.7.8.11.12.13
14.15
1 2, 1 4(BF), 15,16
11,14,15,16
11.14.15.16
14.15.17.21.22.24
11.14.15
2,14
15.24
2.4.10.15
8
12.13
15
15
1,3,4,5,6(BC),7,9
15
15.22.23
15
1.3. 4. 6
15.17.22.24
1.3.4.7.8.9.12.13
3.4.6
1,2,4(BF),6,7,8,9,10,1 3
1 ,4,5(Bne),6,9(BF), 1 3
1.3.5.6.7.8.12.13
8.1 1.12.14.15
14(BF)
15
11.14.15.16.17.18.21.23.24
8.11.14.16
3(BF),4,5,6,7,8
2,5(BF),14
3
6
15,17,21
17
1 (BF),2,4(BF),6,7(BF),9,10
2(Bny),l 1
15.22.23.24
1 ,2(BF),7,8,9, 1 0, 1 4, 1 5,24
1.2.7.9.10.14.23
23.24
16.24
14
12,14(BF),15,16
1,2,4,6,7,9,10,12
8 (BF), 11,12,13,14
1,3, 4, 5, 6, 7
1,3, 4, 5, 6, 7, 8, 9
1994
Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
117
Great Tit Pams major
Green-backed Trr P. monticolus
Yellow-cheeked Tit P. spilonotus
Yellow-browed Trr Sylviparus modestus
Black-throated Tit Aegithalos concinnus
Sand Martin Riparia riparia
Barn Swallow Hirundo rustica
Striated Swallow H. striolaia
Northern House-Martin Delichon urbica
Black-headed Bulbul Pycnonotus airiceps
Black-crested Bulbul P. melanicterus
Red-whiskered Bulbul P. jocosus
Sooty-headed Bulbul P. aurigaster
Stripe-throated Bulbul P. finlaysoni
Flavescent Bulbul P. flavescens
Y ellow-vented Bulbul P. goiavier
Streak-eared Bulbul P. blanfordi
Puff-throated Bulbul Alophoixus pallidus
Ochraceous Bulbul A. ochraceus
Grey-eyed Bulbul Iole propinqua
Ashy Bulbul Hemixos Jlavala
Mountain Bulbul Hypsipetes mcclellandii
Black Bulbul H. leucocephalus
Zitting Cisticola Cisticola juncidis
Golden-headed Cisticola C. exilis
Hill Prinia Prinia airogularis
Rufescent Prinia P. mfescens
Grey-breasted Prinia P. hodgsonii
Y ellow’-bellied Prinia P. flaviventris
Plain Prinia P. inomaia
Oriental White-eye Zosierops palpebrosus
Grey-bellied Tesla Tesia cyaniventer
Pale-foo ted Bush-Warbler Cettia pallidipes
Russet Bush-Warbler Bradypiems seebohnu
Lanceolated Warbler Locustella lanceolata
Black-browed Reed-Warbler Acrocepltalus bistrigiceps
Oriental Reed- Warbler A. orientalis
Thick-billed Warbler A. aedon
Mountain Tailorbird Orthoromus cuculatus
Common Tailorbird O. sutorius
Dark-necked Tailorbird O. atrogularis
Dusky Warbler Phylloscopus fuscatus
Ashy-throated Warbler P. maculipennis
Arctic Warbler P. borealis
Two-barred Warbier P. plumbeiiarsus
Pale-legged Leaf-Warbler P. tenellipes
Blyth’s Leaf-Warbler P. reguloides
White-tailed Leaf-Warbler P. davisoni
White-spectacled Warbler Seicercus affinis
Chestnut-crowned Warbler S. castaniceps
Yellow-bellied Warbler Abroscopus superciliaris
Striated Grassbird Megalums palusrris
Masked Laughingthrush Garmlax perspicillatus
White-crested Laughingthrush G. leucolophus
Lesser Necklaced Laughingthrush G. monileger
24
1,2,4,6,7,8,9,10,12
1,3,4,5,6(BF),7,8
1.3. 5. 7
1.3.4.5.6.7.8.11.12.13
17
2. 10. 14. 15. 16. 17.18. 21. 22. 23. 24
15.17.24
24
14
8.11.14
1,2, 4, 8(BF), 9,1 1,14,15,16,23,24
6.7.8.10.14.23.24
14.15
1.2.3.4.6.7.9.12.13
18
14.17.22.23
15.16
8.11.12.13.14
11.13.14
7.8.11.12.13
1,3,5,6,7,8,12
4. 5. 6. 7. 8. 9.1 1.12.13
14.19.20.23
2,14(Bne),15,16
1,2(BF),3,4,5,6,7(BF),8,9,10,1 1
12,14(BF)
8.11.15.16
2, 1 1 , 1 4(BN), 15,16,18
1.2.7.11.14
8,9,18
1(BF),3,4,5,6,7
1
1.2. 4. 7
15,17
17.21
15.17.18.20.21
15
1.3.4.5.6.7.8.13
15.24
8.9.1 1.12.13.14.15.16
15,17
1.3.6
15.16.24
15
15
1.3. 4.6
1.3.4.5.6.7.8.9.12.13
1.3. 4. 5. 6. 7
1.3.4.5.7.9.13
13.14
15.17.24
15.24
8.11.12.14.15.24
15
118
C. R. ROBSON eial.
Forktail 9
Black-hooded Laughingthrush G. milleii
Black-throated Laughingthrush G. chinensis
White-cheeked Laughingthrush G. vassali
Spot-breasted Laughingthrush G. merulinus
Collared Laughingthrush G. yersini
Abbott’s Babbler Malacocincla abbotii
Buff-breasted Babbler Pellomeum (Trichastoma) tickelli
Spot-throated Babbler Pellomeum albiventre
Puff-throated Babbler P. ruficeps
Scaly-crowned Babbler Malacopteron cinereum
Large Scimitar-Babbler Pomatorhinus hypoleucos
White- browed Scimitar-Babbler P. schisticeps
Red-billed Scimitar-Babbler P. ochraceiceps
Short-tailed Scimitar-Babbler Jabouilleia danjoui
Streaked Wren-Babbler Napoihera brevicaudaia
Eye-browed Wren-Babbler N. epilepidota
Pygmy Wren-Babbler Pnoepyga pusilla
Rufous-capped Babbler Stachyris mficeps
Grey-throated Babbler S. nigriceps
Spot-necked Babbler S. striolata
Striped Tit-Babbler Macronous gularis
Grey-faced Tit-Babbler M. kelleyi
Chestnut-capped Babbler Timalia pileata
Yellow-eyed Babbler Chrysomma sinense
Silver-eared Mesia Leiothrix argentauris
Cutia Cutia nipalensis
White-browed Shrike-Babbler Ptentthius flaviscapis
Chestnut-fronted Shrike-Babbler P. aenobarbus
White-hooded Babbler Gampsorhynchus rufulus
Blue-winged Minla Minla cyatiouroptera
Rufous-winged Fulvetta Alcippe castaneceps
Fulvetta Alcippe sp.
Fulvetta A. (peracemis) grotei
Mountain Fulvetta A. peracensis amiamensis
Rufous-backed Sibia Heterophasia annectans
Black-headed Sibia H. melanoleuca
White-bellied Yuhina Yuhina zamholeuca
Grey-headed Parrotbill Paradoxomis gularis
Rufous-winged Lark Mirafra assamica
Oriental Skylark Alauda gulgula
T hick-billed Flowerpecker Dicaeum agile
Yellow-vented Flowerpecker D. chtysorrheum
Plain Flowerpecker D. concolor
Fire-breasted Flowerpecker D. ignipectus
Scarlet-backed Flowerpecker D. cruemaium
Ruby-cheeked Sunbird Anthreptes singalensis
Purple-naped Sunbird Hypogramma hypogrammicum
Olive-backed Sunbird Nectarinia jugularis
Gould’s Sunbird Aethopyga gouldiae
Fork-tailed Sunbird A. christinae
Black-throated Sunbird A. saturata
Crimson Sunbird A. siparaja
Little SpiDERHUNTER/lracfcnoi/jpi'a longirostra
Streaked Spiderhunter A. magna
Plain-backed Sparrow Passer flaveolus
5.7.12.13
15.24
3(BF), 4, 5,7,8,9,11, 12, 13
3.5.7.12.13
1,3, 4, 5, 6
14(Bne),16
14.15.24
1.2.3.4.5.6.7.8.9.10.13
14
14,15
11,14,16
3.4.6.12.13.14
4.12.13
1,3
12
3.8.12
1,3, 4, 5, 6, 7
1,3,4,5(BF),6,7,8,9,12,13
3.5.6.12.14.15
15
8,1 1,12, 13, 14(BF), 15,16,23, 24
11.12.14.15.16
14.16
14
1.2.3.4.5.6.7.8.9.13
1.3.4.6.7.12.13
1.3.6.7.8.12
1.3.4.5.6.7.8.11.12.13
14
1.3.4.5.6.7.8.13
1,3, 4, 5, 6
1
14,15(Bne)
1.3.4.5.6.7.8.9.11.12.13
7
1,2,3,4(BF),5,6,7,8,12,13
1.3.4.5.6.7.8.9.11.12.13
4, 5, 7, 8
20.23
17.19.20.23
8(BF)
14.15
1 1.15
1.3.4.5.7.8.13
1 1,14,24(BF)
14
14.15
14.15.16.23.24
1.3.4.5.6.7.8.9.12
15.16
13,(15)
11.14.15
14.15
1.3.7.8.11.12.13.14.16
17.18.22.23
1994
Birds recorded during the third Birdlife/Forest Birds expedition in Viet Nam
119
Eurasian Tree Sparrow P. montanus
Yellow Wagtail Motacilla j, Java
Grey Wagtail M. cinerea
Richard’s Pipit Anihus richardi
Paddyfield Piprr A. rufulus
Olive- backed Pipit A. hodgsoni
Streaked Weaver Ploceus manyar
Baya Weaver P. philippinus
Asian Golden Weaver P. hypoxanthus
White-rumped Munia Lonchura striata
Scaly-breasted Munia L. punctulata
Black-headed Munia L. malacca
Vietnamese Greenfinch Carduelis monguiUoti
Red Crossbill Loxia curviroslra
Y eieow-breasted Bunting Emberiza aureola
10.16.17.18.21.22.23.24
15,16,17,21,22
15
15,16
2.6.10.14.17.23.24
4,15
14(Bne)
14(BN),21
14(Bne)
4,8,11, 13, 14(Bne), 15
2,3,4,6,7,10,13,17
14
1,2,4,7,8,9,10(BF)
1,2, 6, 7, 9
15,17,21
ERRATA
Corrections to Robson et at. (1993):
P. 27 Figure: Quy Nhon = Qui Nhon.
P. 28 paragraph 4, line 1: Mount Lang Bian is 2,167 m and not 2,267 m as stated.
P. 47 line 33, should read: CHANGEABLE HAWK-EAGLE Spizaetus cirrhatus 3, (?6)
120
C. R. ROBSON etal.
Forktail 9
1994
FORKTAIL 9 (1993): 121 - 143
121
Birds recorded during a visit to Bhutan
in spring 1993
C. INSKIPP AND T. P. INSKIPP
The birds recorded during a visit to Bhutan between 9 April and 31 May 1993 are documented. A total
of 376 species was recorded of which 33 were apparently first published records for Bhutan, although
previous unpublished records exist for 12 of the latter. A list is given of 1 14 bird species which have
restricted breeding distributions and for which Bhutan may hold significant populations.
Baseline information is lacking on the bird species occurring in Bhutan and
their status and distribution. About 580 species have so far been recorded and
many more are likely to occur. These include 1 14 species for which Bhutan
may support internationally significant breeding populations (see Appendix
I) . Their breeding ranges are restricted to an area encompassing the Himalayas,
north-east India, northern South-East Asia and south-west China. The
boundaries of this area are to some extent arbitrary, but do coincide roughly
with the mountain ranges contiguous with the Himalayas and its neighbouring
lowlands. Many of these species are temperate forest birds. This is because
a high proportion of the remaining temperate forests in the Indian subcontinent
lie in Bhutan.
A programme of wildlife inventory compilation alongside socio-economic
assessment of communities living adjacent to protected areas is currently
being carried out by the Royal Government of Bhutan Department of Forests
and the WWF Bhutan Programme. The main objectives are to improve
knowledge of Bhutan’s natural environment, to help plan and establish a
system of protected areas, and to develop an integrated conservation and
development programme in protected areas in Bhutan. In April and May
1993 we were very fortunate to be invited to join the group of field workers
engaged in this programme. Together with Kado Tshering and Pema
Gyaltshen from the Department of Forests, we formed the avifauna team.
We coordinated our activities with those of two other teams who made
surveys of fauna, flora and socio-economic factors.
During our stay in Bhutan between 9 April and 31 May we recorded 331
bird species during the survey and an additional 45 species elsewhere in
country7. A swiftlet Collocalia species seen on several occasions may be an
undescribed species. A list of recorded species, their habitats and altitudinal
ranges are given in Appendix II. Thirty-three species were found for which
there are no previously published records for Bhutan. Four species which
have been identified as globally threatened by Collar and Andrew (1988)
122
C. INSKIPP and T. P. INSKIPP
Forktail 9
Figure 1. Bhutan, showing locations mentioned in text..
1994
Birds recorded during a visit to Bhutan in spring 1993
123
were recorded: Rufous-necked Hornbill Aceros nipalensis , Pallas’s Fish-Eagle
Haliaeetus Ieucoryphus, White-bellied Heron Ardea insignis and Rufous-
throated Wren-Babbler Spelaeomis caudatus. A total of 64 species for which
Bhutan may support internationally significant breeding populations were
also found.
After a few days in the capital, Thimphu (2,400 m) we drove to the Royal
Manas National Park via Phuntsholing (350 m) on the southern border, and
West Bengal and Assam in India. The wide braided channels and shingle
islands of the T orsa river at Phuntsholing hold a wide variety of wetland birds,
especially passage migrants. Between 17 and 25 April we recorded 16 new
species for the country in Manas. Much of our time was spent in primary
tropical evergreen and moist semi-evergreen forests.
We then walked north over the Himalayan foothills through the proposed
link area between Manas National Park and the proposed Black Mountains
Nature Reserve reaching Tingtibi (650 m) on 2 May. Apart from several
villages and associated clearings for cultivation, the hills are largely clothed
in primary broadleaved tropical and subtropical evergreen and moist semi¬
evergreen forests with patches of bamboo. Between Tshanglajong (1,065 m)
and Tingtibi there are extensive stands of tall bamboo. The broadleaved
evergreen forests and bamboo stands in the tropical and subtropical zones
were found to be particularly interesting for birds and must of special
importance ornithologically in the Indian subcontinent. These vegetation
types, which are still substantially intact in Bhutan, are now scarce or absent
in other Himalayan countries because of deforestation.
The Rufous-necked Hornbill, appeared to be fairly common in the
broadleaved evergreen forests. Other birds recorded which have restricted
ranges and are dependent on evergreen forest include Collared Treepie
Dendrocitta frontalis. Spotted Wren-Babbler Spelaeomis formosus, Yellow-
throated Fulvetta Alcippe cinerea and White-naped Yuhina Yuhina bakeri.
The bamboo stands between Tshanglajong and Tingtibi are also important
for several specialist birds which require this habitat, including the Lesser
Rufous-headed Parrotbill Paradoxomis atrosuperciliaris of the very distinct
subspecies oatesi. Apart from recent records in Bhutan this subspecies has
only been previously recorded in Darjeeling and Sikkim in the last century.
The Yellow-vented Warbler Phylloscopus cantator, which has a very restricted
range, was found to be common in evergreen tropical and subtropical forests,
and was regularly recorded in semi-evergreen forests. Most birds recorded
were singing and presumably holding breeding territories.
On five days and around three villages between 650 m and 1 ,395 m we saw
a swiftlet Collocalia species, probably a migrant, which we could not identify.
The birds did not resemble any specimens of Collocalia species which we
subsequently examined in the collection of the British Museum (Natural
History). The tail furcation was similar to that of Himalayan Swiftlet
124
C. INSKIPP and T. P. INSKIPP
Forktail 9
Collocalia brevirostris, but the bird was slightly larger and longer- winged. The
plumage was generally blackish, with only a slightly paler rump, unlike the
grey coloration and more contrasting paler rump of Himalayan Swiftlet. The
flight was stronger, more direct and less ‘fluttering’ than the last species.
After spending a rest day at T ongsa (2,200 m) in central Bhutan, we carried
out a survey in the proposed Black Mountains Nature Reserve between 7 and
22 May, covering the loop from Phobjika (2,780 m) to Ada (1,280 m) and
back to Phobjika via the Gele La pass (3,630 m) and the Harachhu valley
(1,125 - 1,445 m). The survey was largely in primary subtropical and
temperate forests, mainly comprising broadleaves or mixed broadleaves/
conifers with extensive stands of bamboo in the wetter areas and Chir Pine
Pinus roxbarghii covering drier slopes in the subtropical zone.
On this trek we had some logistical difficulties which prevented us
adequately covering the higher altitude areas in the temperate zone. Many
noteworthy bird species were still recorded in temperate forests however,
including as many as 37 species for which Bhutan may support internationally
significant breeding populations. One of these was the Satyr Tragopan
Tragopan satyra which appeared to be fairly common in mixed coniferous/
broadleaved forests between 2,805 m and 3,430 m. In its range outside of
Bhutan this species is declining because of hunting and deforestation. As we
left Phobjika and drove over the northern rim of the valley there was a sudden
heavy shower and we were amazed to see a Whimbrel Numenius phaeopus by
the roadside, grounded by the rain. This record is apparently the first for
Bhutan.
The subtropical forests along the trail between Phobjika and Ada were
found to be significantly less species-rich than those between Manas and
Tingtibi. The former forests are drier and mainly semi-evergreen with only
patches of evergreen character compared to the largely evergreen forests
south of Tingtibi. One notable species in the subtropical semi-evergreen
forests between Phobjika and Ada was the Yellow-vented Warbler, which
was found to be fairly common. Three globally threatened species were
recorded in the relatively moist forests around Ada: Rufous-necked Hornbill,
White-bellied Heron and Rufous-throated Wren-Babbler. The heron, which
was seen by a small lake at Ada, is of special interest because it has a restricted
range, and also because there are very few recent world records of the species.
Three pheasant chicks crossed our path near Ada lake and an anxious pair
of Kalij Pheasants Lophura leucomelanos made a noisy distraction display,
running in circles around us, only a few metres away and calling. The male
was all black, a distinctive characteristic of subspecies moffitti. This is the first
record of moffitti in the wild.
On 30 May we had a day’s walk from Thimphu up to the Dochu La pass
(3,530 m) via Tashigong monastery (3,265 m). The highlight was a male
1994
Birds recorded during a visit to Bhutan in spring 1993
125
Blue-fronted Robin Cinclidium frontale, a new species for Bhutan, which was
feeding on the ground amongst mugwort Artemisia dubia and bushes at the
edge of mixed forest close to the monastery.
ANNOTATED LIST OF SELECTED SPECIES
BLACK PARTRIDGE Francolinus francolinus One heard on 20 April at
Manas National Park (350 m). Previously mentioned for Bhutan only by
Ripley (1982), but apparently based on supposition (Ali et al. in press).
INDIAN PEAFOWL Pavo cristatus Two heard on 18 April at Manas
National Park (250 m). Apparently the first published record for Bhutan.
JAPANESE QUAIL Cotumix japonica Recorded on 7 and 20-22 May in
wheat fields in the Phobjika valley (2,800 m), with maximum of three heard
and one seen on 22 May. Previously also recorded from Bhutan in the
breeding season: collected by F. M. Bailey on 5 July 1 922 (Bailey 1 938) and
recorded singing in suitable breeding habitat in 1990 by F. A. Clements in
Bumthang on 29 April, Ugyencholing on 1 May and Gangtey Gompa on 9
May (Clements 1992). These Bhutanese birds were probably breeding and
were 2,000 km south-west of the nearest recorded nesting area in China,
although a nest with eggs probably belonging to this species was found in
Myanmar on 30 October 1935 (Livesey 1936).
SATYR TRAGOPAN Tragopan satyra Two heard on the Gele La on 7 and
8 May above 3,000 m, one male in the Phobjika valley on 20 May (2,805 m)
and four males and one female near Tashigong monastery, DochuLa (3,165-
3,430 m). There are several previous published records: Ali and Ripley
(1987), Clements (1992), Inskipp and Inskipp (1993), Ludlow and Kinnear
(1937), Singh (1985) and Vas (1986).
KALIJ PHEASANT Lophura leucomelanos moffitti An all black adult male,
with a female and three chicks on 16 May near Ada (1,280 m). This is
apparently the first observation of the moffitti subspecies in the wild. A bird
collected from central Bhutan and stated to be of this subspecies by Ali and
Ripley (1987), has now proved to be an intergrade between melanota and
lathami (Ali et al. in press).
NORTHERN SHOVELER Anas clypeata A flock of 30 on 17 April flying
up the Manas river in Manas National Park (250 m). Apparently the first
published record for Bhutan, although previously recorded by Johnson
(1993).
GARGANEY Anas querquedula A flock of ten on 1 7 April on the Torsa river
at Phuntsholing (350 m). Apparently the first published record for Bhutan,
although previously seen by Ali et al. (in press) and A. Pain (verbally 1993).
BLUE-EARED BARBET Megalaima australis Recorded from 20 - 23 April
at Manas National Park (300-450 m) with a maximum of six on 22 April.
126
C. INSKIPP and T. P. INSKIPP
Forktail 9
Previously mentioned only by Ali and Ripley (1987) and Ripley (1982), but
apparently based on supposition (Ali et al. in press).
BLACK-BACKED KINGFISHER Ceyx erithacus Two on 21 and 22 April
at Manas National Park (450 m). Previously mentioned for Bhutan only by
Ali and Ripley (1987) and Ripley (1982), but apparently based on supposition
(Ali et al. in press).
RUDDY KINGFISHER Halcyon coromanda Recorded from 20 - 22 April
at Manas National Park (450-510 m), with a maximum of three on 21 April.
Previously mentioned for Bhutan by Ali and Ripley (1987) and recorded by
Ali et al. (in press).
PIED KINGFISHER Ceryle mdis One on 18 April at Manas National Park
(250 m). Previously listed for Bhutan only by Ali and Ripley (1987), but
apparently based on supposition (Ali et al. in press).
RUFOUS-NECKED HORNBILL Aceros nipalensis Recorded on 19, 24
and 25 April at Manas National Park (300-635 m), with a maximum of five
on 25 April; one on 27 April at Dalim (7 1 0 m), three on 30 April at Subrang
( 1 ,400 m), one on 1 May between Zurphey and Tshanglajong ( 1 ,320 m), one
on 2 May between Tshanglajong and Tingtibi, and one on 17 and 18 May
at Ada (1,280 m). Apparently fairly common in tropical and subtropical
broadleaved evergreen forests. Previously recorded by Clements (1992),
Inskipp and Inskipp (1993), Ali et al. (in press) and Johnson (1993), and
listed by Ali and Ripley (1987) and Ripley (1982).
ASIAN EMERALD CUCKOO Chrysococcyx maculatus Recorded from 20
- 22 April at Manas National Park (300-450 m), with a maximum of four on
22 April. One on 5 May at Tongsa (2,200 m). Singles at Lawa (1,125 m) on
1 1 and 14 May. Apparently the first published records for Bhutan, although
previously recorded by Mills (1989).
GREATER COUCAL Centropus sinensis One on 20 and two on 22 April at
Manas National Park (400 m), two on 12 May in the Harachhu valley (1,445
m) and one to two at Nashina on 15 and 16 May (1,515 m, 1,600 m).
Previously mentioned for Bhutan only by Ali and Ripley (1987), but
apparently based on supposition (Ali et al. in press).
SWIFTLET Collocalia Four seen on 27 and 28 April at Tshobrang (1,395
m), six on 1 May and 10 on 2 May at Tshanglajong (1,065 m) and one on
3 May at Tingtibi (650 m).
CRESTED TREESWIFT Hemiproctte coronata One on 20 April at Manas
National Park (350 m). Apparently the first published record for Bhutan.
ORIENTAL SCOPS-OWL Otus sunia Two heard on 18 and 19 April at
Manas National Park (250 m). Previously mentioned only by Ali and Ripley
(1987) and Ripley (1982), but apparently based on supposition (Ali et al. in
press).
1994
Birds recorded during a visit to Bhutan in spring 1993
127
BROWN WOOD-OWL Stnx leptogrammica One heard on 1 0 May at Nehi
(2,440 m). Apparently the first published record for Bhutan, but previously
recorded by Ali et al. (in press).
BROWN HAWK-OWL Ninox scutulata One or two heard at Manas
National Park from 18 to 22 April (250-450 m). Previously mentioned only
by Ali and Ripley (1987) and Ripley (1982), but apparently based on
supposition.
RED COLLARED-DOVE Streptopelia tranquebanca Three on 23 April at
Manas National Park (380 m). Apparently the first published record for
Bhutan, but previously recorded by All et al. (in press).
ORANGE-BREASTED GREEN-PIGEON Treron bicincta Three on 19
April and 2 on 20 April at Manas National Park (250 m). Previously listed
for Bhutan only by Ripley ( 1 982), but apparently based on supposition (Ali
et al. in press).
POMPADOUR GREEN-PIGEON Treron pompadora Two on 23 April at
Manas National Park (380 m). Apparently the first published record for
Bhutan.
THICK-BILLED GREEN-PIGEON Treron curvirostra One on 20 April at
Manas National Park (250 m). Apparently the first published record for
Bhutan, although previously seen by Jepson (1989).
WHIMBREL Numenius phaeopus One on 22 May on the northern rim of the
Phobjika valley (3,250 m). Apparently the first published record for Bhutan.
COMMON GREENSHANK Tringa nebularia One on 17 April at
Phuntsholing (350 m). Previously recorded by Inskipp and Inskipp (1993)
and Ali et al. (in press).
EURASIAN THICK-KNEE Burhinus oedicnemus Two on 18 April at
Manas National Park (250 m). Apparently the first published record for
Bhutan.
LITTLE RINGED PLOVER Charadrius dubius One on 17 April by the
Torsa river at Phuntsholing (350 m). Apparently the first published record
for Bhutan, although previously seen by Johnson (1993).
SMALL PRATINCOLE Glareola lactea Thirty on 16 April and 10 on 17
April by the Torsa river at Phuntsholing (350 m). Apparently the first
published record for Bhutan, although previously recorded by Ali et al. (in
press).
GREAT BLACK-HEADED GULL Larus ichthyaetus Two on 17 April by
the Torsa river at Phuntsholing (350 m). Apparently the first published
record for Bhutan, although previously seen by Johnson (1993).
RIVER TERN Sterna aurantia Five on 1 9 April flying up the Manas river in
Manas National Park (250 m). Apparently the first published record for
Bhutan.
128
C. INSKIPP and T. P. INSKIPP
Forktail 9
PALLAS’S FISH-EAGLE Haliaeetus leucoryphus One on 1 8 April at Manas
National Park (250 m). The previous published records are Inskipp and
Inskipp (1993) and Ludlow and Kinnear (1937); also seen by Ali et al. (in
press), Barber (1990-1991) and Johnson (1993).
WHITE-RUMPED VULTURE Gyps bengalensis Recorded on 1 6 and 1 7
April at Phuntsholing (350 m), 1 8-20 April at Manas National Park (250 m)
and 1 1 May in the Harachhu valley ( 1 ,200 m), with a maximum of 1 0 on 18
April. Previously recorded by Inskipp and Inskipp (1993).
SWWGRA Accipiter badius One on 10 May in the Harachhu valley (1,125 m)
and one on 18 May at Ada (1,280 m). Previously recorded by Inskipp and
Inskipp (1993).
BOOTED EAGLE Hieraaetus pennatus One on 18 April at Manas National
Park (250 m). Apparently the first published record for Bhutan, although
previously seen by Mills (1989).
LITTLE CORMORANT Phalacrocorax niger Thirty on 1 6 April and 1 0 on
17 April by theTorsa river at Phuntsholing (350 m). Previously recorded by
Inskipp and Inskipp (1993).
LITTLE EGRET Egretta garzetta One on 1 6 April and three on 1 7 April by
the Torsa river at Phuntsholing (350 m). Previously recorded by Inskipp and
Inskipp (1993).
GREY HERON Ardea cinerea One on 17-19 April by the Manas river in
Manas National Park (250 m). Previously only listed for Bhutan by Scott
(1989).
WHITE-BELLIED HERON Ardea insignis One on 1 6 and 1 7 April by Ada
Lake (1,280 m). Previously recorded only by Inskipp and Inskipp (1993).
INTERMEDIATE EGRET Mesophoyx intermedia One on 1 7 April by the
Torsa river at Phuntsholing (350 m). Apparently the first published record
for Bhutan.
CATTLE EGRET Bubulcus ibis Fifty on 1 6 April and 20 on 1 7 April by the
Torsa river at Phuntsholing (350 m). Previously recorded by Inskipp and
Inskipp (1993) and Ali et al. (in press).
STRIATED HERON Butorides striatus One on 1 7 April by the Manas river
at Manas National Park (250 m). Apparently the first published record for
Bhutan.
COLLARED TREEPIE Dendrocitta frontalis One on 24 April and five on 25
April at Manas National Park (5 1 0-635 m), two on 26 April near Dalim (620
m) and three on 27 April between Dalim and T shobrang (710m). Previously
recorded by Jepson (1988) and Inskipp and Inskipp (1993). Listed for
Bhutan by Ripley (1982), but apparently based on supposition (Ali et al. in
press).
LARGE CUCKOO-SHRIKE Coracina macci One to two on 20, 22 and 23
April at Manas National Park (350-450 m) . Previously recorded by Clements
(1992).
1994
Birds recorded during a visit to Bhutan in spring 1993
129
ROSY MINIVET Pericrocotus roseus One on 20 April and two on 22 April
at Manas National Park (300-450 m). Apparently the first published records
for Bhutan.
CROW-BILLED DRONGO Dicrurus annectans Recorded on 1 1 dates
between 1 9 April and 1 4 May between 300 m and 1450 m, with a maximum
of seven on 22 April at Manas National Park between 350 and 480 m.
Apparently fairly common. Previously recorded by Inskipp and Inskipp
(1993), and listed by Ali and Ripley (1987), but the latter is apparently based
on supposition (Ali et al. in press).
LESSER SHORTWING Brachypteryx stellata Four on 28 April at T shobrang
(1,595 m), one on 7 May between Phobjika and Khebitanka (2,725 m) five
on 9 May above Laphu Gang (3,150-3,280 m) and one on 20 May above
Tarana (2,435 m). Previously mentioned only by Ali and Ripley (1987) and
Ripley (1982), but apparently based on supposition.
ASIAN BROWN FLYCATCHER Muscicapa dauurica One on 2 1 April at
Manas National Park (450 m). Previously recorded by Inskipp and Inskipp
(1993), and listed by Ali and Ripley (1983), but the latter is apparently based
on supposition (Ali et al. in press).
PALE-CHINNED FLY CATCHER Cyomis poliogenys Three on 22 April at
Manas National Park (400 m), one on 16 May between Nashina and Ada
(1,335 m) and two on 18 May near Ada (1,260 m). Previously listed for
Bhutan only by Ali and Ripley (1987) and seen by Ali et al. (in press).
BLUE-FRONTED ROBIN Cinclidium frontale A male on 30 May by
Tashigong monastery, Dochu La (3,265 m). Apparently the first published
record for Bhutan. This species has rarely been observed in the field and is
very poorly known (Redman 1992).
VELVET-FRONTED NUTHATCH Sitta frontalis Two on 26 April at
Manas National Park (350 m). Previously listed only by Ali and Ripley
(1987) and Ripley (1982), apparently based on supposition (Ali et al. in
press).
GREY-CROWNED PRINIA Prinia cinereocapilla Three on 3 May at
Tingtibi (700 m), two on 1 5 May at Nashina (1,220 m) and one on 1 7 May
at Ada (1,300 m). Previously listed only by Ali and Ripley (1987) and Ripley
(1982), but apparently based on supposition (Ali et al. (in press).
BLYTH’S REED-WARBLER Acrocephalus dumetorum One to two on 21-
23 April at Manas National Park (380-450 m), two on 26 April at Dalim (7 1 0
m), one on 28 April between Tshobrang and Ponchela ( 1 ,400 m) and one on
30 April between Subrang and Zurphey (1,460 m). Previously listed for
Bhutan by Ali and Ripley (1987), and recorded by Ali et al. (in press).
Apparently fairly common.
YELLOW- VENTED WARBLER Phylloscopus cantator Recorded on 17
dates between 19 April and 1 8 May from 300 m to 1,540 m, with a maximum
130
C. INSKIPP and T. P. INSKIPP
Forktail 9
of 1 6 on 24 April in Manas National Park from 380 to 5 1 0 m. Most common
in broadleaved evergreen forest. Previously listed for Bhutan by Abdulali
(1986) and Ali and Ripley (1987), and recorded by Ali et al. (in press) and
Johnson (1993).
RUFOUS-THROATED WREN-BABBLER Spelaeomis caudatus One on
19 May above Ada (1,630 m). Previously listed for Bhutan by Abdulali
(1983) and Ali and Ripley (1987), and recorded by Ludlow and Kinnear
(1937), Ludlow and Kinnear (1944) and Ali et al. (in press).
SPOTTED WREN-BABBLER Spelaeomis fonnosus One on 3 May at
Tingtibi (770 m). Previously listed for Bhutan by Abdulali (1983) and Ali
and Ripley (1987), and recorded by Ludlow and Kinnear (1937) and Ali et
al. (in press).
WHITE-HOODED BABBLER Gampsorhynchus rufulus Four on 2 May
between Tshanglajong and Tingtibi (915m). Apparently the first published
record for Bhutan, although previously seen by Anon. (1992).
YELLOW-THROATED FULVETTA Alcippe cinerea Ten on 28 April
above Tshobrang (1595 m). Previously listed for Bhutan by Abdulali (1984)
and Ali and Ripley (1987), and recorded by Inskipp and Inskipp (1993),
Ludlow and Kinnear (1944) and Ali et al. (in press).
WHITE-NAPED YUHINA Yuhina bakeri Three on 25 April at Manas
National Park (550 m), three on 25 April between Manas and Dalim (580
m), two carrying nest material on 26 April at Dalim (620 m) and two on 27
April between Dalim and Tshobrang (740 m). Previously listed for Bhutan
by Abdulali (1969-1992) and Ali and Ripley (1987), and recorded by
Clements (1992), Inskipp and Inskipp (1993), Ali et al. (in press) and
Johnson (1993).
LESSER RUFOUS-HEADED PARROTBILL (BLACK-BROWED
PARROTBILL) Paradoxomis atrosuperciliaris Two on 27 April at Dalim
(710 m) and 1 5 on 2 May between Tshanglajong and Tingtibi (915 m) were
of the western race oatesi, which lacks a black eyebrow, hence the choice of
English name. Apparently the first published record for Bhutan, although
previously seen by Anon. (1992) and Johnson (1993).
WHITE-BROWED WAGTAIL Motacilla maderaspatensis Two on 17 April
by the Torsa river at Phuntsholing (350 m) and one on 17 April by the Manas
river at Manas National Park (250 m). Previously recorded by Inskipp and
Inskipp (1993) and Ali et al. (in press).
BLACK-FACED BUNTING Emberiza spodocephala One on 30 April in
fields at Subrang (1,400 m). Apparently the first published record for
Bhutan.
1994
Birds recorded during a visit to Bhutan in spring 1993
131
We are very grateful to the Worldwide Fund for Nature Bhutan, particularly Mingma Norbu Sherpa and
Tobgay Sonam, and the Royal Bhutan Department of Forests for inviting us to join the wildlife inventory
team in Bhutan and for arranging the logistics of our visit. We would also like to warmly thank the
Bhutanese who accompanied us in the field for their invaluable assistance. Special thanks go to Kado
Tshering, Assistant District Forest Officer, who organised our team as well as taking part in the
ornithological work, and to Pema Namgay, Warden of the Royal Manas National Park for organising
our visit to the park.
REFERENCES
Anon. (1992) Manas... and the jungles of Bhutan, p.9 in Naturetrek 1993. Unpublished.
Abdulali, H. ( 1 983) A catalogue of the birds in the collection of Bombay Natural History Society - 25
Muscicapidae (Timaliinae) (part). J. Bombay Nat. Hist. Soc. 79: 336-360.
Abdulali, H. ( 1984) A catalogue of the birds in the collection of Bombay Natural History Society - 28
Muscicapidae (Timaliinae) (contd.). J. Bombay Nat. Hist. Soc. 80: 349-369.
Abdulali, H. ( 1 986) A catalogue of the birds in the collection of Bombay Natural History Society - 3 1
Muscicapidae (Sylviinae) (contd.). J. Bombay Nat. Hist. Soc. 83: 339-359.
Ali, S. and Ripley, S. D. (1987) Compact edition of the Handbook of the birds of India and Pakistan. Delhi:
Oxford University Press.
Ali, S., Biswas, B. and Ripley, S. D. (in press) The birds of Bhutan. Rec. Zool. Surv. India, Occ. Pap. 136.
Bailey, F. M. (1938) Specimens collected in Bhutan in 1922 deposited in British Museum (Natural
History).
Barber, I. (1990-1991) Unpublished notes.
Clements, F. A. (1992) Recent records of birds from Bhutan. Forktail 1:57-73.
Collar, N. J. and Andrew, P. (1988) Birds to watch: the ICBP world checklist of threatened birds. ICBP
Technical Publication No. 8.
Inskipp, C. and Inskipp, T. P. (1993) Birds recorded during a visit to Bhutan in autumn 1991 . Forktail
8:97-112.
Jepson, P. (1988) Naturetrek. Bhutan bird list. 17th October to 1st November 1988. Unpublished.
Johnson, D. L. (1993) Birds recorded in Bhutan, 17 March to 3 April 1993. Unpublished.
Livesey, T. R. (1936) Does the Japanese Grey Quail {Cotamix c. japonica Temm. & Schleg.) breed in
the Shan States? J. Bombay Nat. Hist. Soc. 38: 830-831.
Ludlow, F. and Kinnear, N. B. ( 1 937) The birds of Bhutan and adjacent territories of Sikkim and Tibet.
Ibis (14)1:1-46, 249-293, 467-504.
Ludlow, F. and Kinnear, N. B. (1944) The birds of South-eastern Tibet. Ibis 86:43-86, 176-208, 348-
389.
Mills, D. G. H. (1989) Bhutan’s Bumthang valley - April/May 1989: a list of birds and mammals
recorded. Naturetrek. Unpublished.
Redman, N. (1992) Little-known bird. Blue-fronted Robin. Oriental Bird Club Bull. 16: 33-35.
Ripley, S. D. (1982) Synopsis of the birds of India and Pakistan . Bombay: Bombay Natural History Society.
Scott, D. A. (ed.) (1989) A directory of Asian wetlands. Gland, Switzerland and Cambridge: IUCN.
Singh, N. (1985) Bhutan: a kingdom in the Himalayas. 3rd ed.
Vas, E. A. (1986) The dragon kingdom: journeys through Bhutan. New Delhi: Lancer International.
Carol Inskipp and Tim Inskipp, 1 Hemeside, March Road, Welney, Wisbech, Cambs. PE 14 9SB, UK.
132
C. INSKIPP and T. P. INSKIPP
Forktail 9
APPENDIX I
BIRD SPECIES FOR WHICH BHUTAN MAY HOLD
SIGNIFICANT BREEDING POPULATIONS
1994
Birds recorded during a visit to Bhutan in spring 1993
133
134
C. INSKIPP and T. P. INSKIPP
Forktail 9
Carpodacus edwardsii
Carpodacus thura
Carpodacus rubicilloides
Pinicola subhimachalus
Haematospiza sipahi
Pyrrhula erythrocephala
Mycerobas affinis
Mycerobas melanozanthos
Pyrrhoplecies epauleita
Dark-rumped Rosefinch
White-browed Rosefinch
Streaked Rosefinch
Crimson-browed Finch
Scarlet Finch
Red-headed Bullfinch
Collared Grosbeak
Spot-winged Grosbeak
Gold-naped Finch
+ = species recorded during survey
[+] = species recorded elsewhere in Bhutan in April and May 1993
+
APPENDIX II
BIRDS RECORDED IN APRIL AND MAY 1993
Localities
6
19
u
u
21
21.31.33
33
6,8
8.15.29
6,7,9,11,13,27
6
6
6
350 5
350 5
6
6.12.25.29
3,20-22,24-26,
28.33
3,21,30
6
6.8.10.25.29
6.7.13.25.29
6-9,13,28-30
6
10.13.29
u
5,6
u
u
6
1994
Birds recorded during a visit to Bhutan in spring 1993
135
ORIENTAL P1ED-HORNB1LL Anthracoceros albirostris
GREAT HORNB1LL Buceros bicomis
RUFOUS-NECKED HORNBILL Aceros nipalensis
WREATHED HORNBILL A ceros undulatus
EURASIAN HOOPOE Upupa epops
RED-HEADED TROGON Harpactes erythrocephalus
INDIAN ROLLER Coracias benghalensis
DOLLARBIRD Eurystomus orientalis
COMMON KINGFISHER Alcedo atthis
BLACK-BACKED KINGFISHER Ceyx eriihacus
RUDDY KINGFISHER Halcyon coromanda
WHITE-THROATED KINGFISHER Halcyon smymensis
CRESTED KINGFISHER Megaceryle lugubris
PIED KINGFISHER Ceryle rudis
BLUE-BEARDED BEE-EATER Nyctyomis aihertoni
CHESTNUT-HEADED BEE-EATER Merops leschenaulu
CHESTNUT- WINGED CUCKOO Clamator coromandus
LARGE HAWK-CUCKOO Cuculus sparverioides
COMMON HAWK-CUCKOO Cuculus varius
INDIAN CUCKOO Cuculus micropterus
COMMON CUCKOO Cuculus canorus
ORIENTAL CUCKOO Cuculus saturatus
LESSER CUCKOO Cuculus polioceplialus
GREY-BELLIED CUCKOO Cacomantis passerinus
ASIAN EMERALD CUCKOO Chrysococcyx maculatus
DRONGO CUCKOO Surniculus lugubris
GREEN-BILLED MALKOHA Phaenicophacus trisiis
GREATER COUCAL Centropus sinensis
LESSER COUCAL Centropus bengalensis
RED-BREASTED PARAKEET Psittacula alexandri
HIMALAYAN SWIFTLET Collocalia brevirostris
ASIAN PALM-SWIFT Cypsiurus balasiensis
FORK-TAILED SWIFT Apus pacificus
HOUSE SWIFT Apus nipalensis
CRESTED TREESWIFT Hemiprocne coronata
MOUNTAIN SCOPS-OWL Otus spilocephalus
ORIENTAL SCOPS-OWL Otus sunia
COLLARED SCOPS-OWL Otus lempiji
TAWNY FISH-OWL Ketupa flavipes
BROWN WOOD-OWL Strix leptogrammica
TAWNY OWL Strix aluco
COLLARED OWLET Glaucidium brodtci
6,8,10,11,14,20,25
ASIAN BARRED OWLET Glaucidium cuculoides
BROWN HAWK-OWL Ninox scutulata
GREY NIGHTJAR Caprimulgus indicus
LARGE-TAILED NIGHTJAR Caprimulgus macrurus
SWIFTLET Collocalia species
WHITE-THROATED NEEDLETAIL Hirundapus caudacutus
136
C. INSKIPP and T. P. INSKIPP
Forktail 9
ROCK PIGEON Columba livia
SNOW PIGEON Columba leuconota
SPECKLED WOOD-PIGEON Columba hodgsonii
ORIENTAL TURTLE-DOVE Streptopelia oriemalis
SPOTTED DOVE Streptopelia chinensis
RED COLLARED-DOVE Streptopelia tranquebarica
EURASIAN COLLARED-DOVE Streptopelia decaocto
BARRED CUCKOO-DOVE Macropygia unchall
EMERALD DOVE Chalcophaps indiea
ORANGE-BREASTED GREEN-PIGEON Treroti bicincta
POMPADOUR GREEN-PIGEON Treroti pompadora
THICK-BILLED GREEN-PIGEON Treroti curvirostra
PIN-TAILED GREEN-PIGEON Treroti apicauda
WEDGE-TAILED GREEN-PIGEON Treroti sphenura
MOUNTAIN IMPERIAL-PIGEON Ducula badia
EURASIAN WOODCOCK Scolopax rusticola
WHIMBREL Numenius phaeopus
COMMON GREENSHANK Tringa nebularia
GREEN SANDPIPER Tringa ochropus
COMMON SANDPIPER Tringa hypoleucos
EURASIAN THICK-KNEE Burhinus oedicnemus
LITTLE RINGED PLOVER Charadrius dubius
RIVER LAPWING Vanellus duvaucelii
RED-WATTLED LAPWING Vanellus indicus
SMALL PRATINCOLE Glareola lactea
GREAT BLACK-HEADED GULL Larus ichthyaetus
RIVER TERN Sterna aurantia
OSPREY Pandion haliaetus
ORIENTAL HONEY-BUZZARD Pemis ptilorhyncus
BLACK KITE Milvus migrant
BLACK-EARED KITE Milvus lineatus
PALLAS’S FISH-EAGLE Haliaeetus leucoryphus
WHITE-RUMPED VULTURE Gyps bengalensis
HIMALAYAN GRIFFON Gyps himalayensis
CRESTED SERPENT-EAGLE Spilomis cheela
CRESTED GOSHAWK Accipiter rrivirgaius
SHIKRA Accipiter badius
BESRA Accipiter virgatus
EURASIAN SPARROWHAWK Accipiter nisus
COMMON BUZZARD Buteo buteo
BLACK EAGLE Icrinaetus malayensis
STEPPE EAGLE Aquila nipalensis
BOOTED EAGLE Hieraaetus pennatus
RUFOUS-BELLIED EAGLE Hieraaetus kienerii
MOUNTAIN HAWK-EAGLE Spizactus nipalensis
COLLARED FALCONET Microhierax caerulescens
COMMON KESTREL Falco tinnunculus
EURASIAN HOBBY Falco subbuteo
PEREGRINE FALCON Falco peregrinus
LITTLE CORMORANT Phalacrocorax niger
GREAT CORMORANT Phalacrocorax carbo
LITTLE EGRET Egretta garzetta
1994
Birds recorded during a visit to Bhutan in spring 1993
137
138
C. INSKIPP and T. P. INSKIPP
Forktail 9
30
1994
Birds recorded during a visit to Bhutan in spring 1993
139
140
C. INSKIPP and T. P. INSKIPP
Forktail 9
1994
Birds recorded during a visit to Bhutan in spring 1993
141
CHESTNUT-TAILED MINLA Minla strigula
RED-TAILED MINLA Minla ignotincta
GOLDEN-BREASTED FULVETTA Alcippe chrysotis
YELLOW-THROATED FULVETTA Alcippe cinerea
RUFOUS-WINGED FULVETTA Alcippe castaneceps
WHITE-BROWED FULVETTA Alcippe vinipectus
NEPAL FULVETTA Alcippe tiipalensis
RUFOUS SIBIA Heterophasia capistraia
LONG-TAILED SIBIA Heterophasia picaoides
STRIATED YUHINA Yuhina castaniceps
WHITE-NAPED YUHINA Yuhina bakeri
WHISKERED YUHINA Yuhina flavicollis
STRIPE-THROATED YUHINA Yuhina gularis
RUFOUS-VENTED YUHINA Yuhina occipitalis
BLACK-CHINNED YUHINA Yuhina nigrimenta
FIRE-BREASTED FLOWERPECKER Dicaeum ignipectus
RUBY-CHEEKED SUNBIRD Anthreptes singalensis
MRS GOULD’S SUNBIRD Aethopyga gouldiae
GREEN-TAILED SUNBIRD Aethopyga nipalcnsis
BLACK-THROATED SUNBIRD Aethopyga saturata
CRIMSON SUNBIRD Aethopyga siparaja
STREAKED SPIDERHUNTER Arachnothera magna
HOUSE SPARROW Passer domes ticus
RUSSET SPARROW Passer rutilans
EURASIAN TREE SPARROW Passer montanus
WHITE WAGTAIL Motacilla alba
WHITE-BROWED WAGTAIL Motacilla maderaspatensis
CITRINE WAGTAIL Motacilla citreola
GREY WAGTAIL Motacilla cinerea
PADDYFIELD PIPIT Anthus rufulus
OLIVE-BACKED PIPIT Anthus hodgsoni
ROSY PIPIT Anthus roseatus
RUFOUS-BREASTED ACCENTOR Prunella strophiata
WHITE-RUMPED MUNIA Lonchura striata
TIBETAN SERIN Serinus thibetanus
YELLOW-BREASTED GREENFINCH Carduelis spinoides
PLAIN MOUNTAIN-FINCH Leucosticte nemoricola
COMMON ROSEFINCH Carpodacus erythrinus
SCARLET FINCH Haematospiza sipahi
RED CROSSBILL Loxia curvirostra
WHITE-BELLIED YUHINA Yuhina zantholeuca
GREY-HEADED PARROTBILL Paradoxomis gularis
BLACK-THROATED PARROTBILL Paradoxomis nipalensis
LESSER RUFOUS-HEADED
PARROTBILL Paradoxomis atrosuperciliaris
SAND LARK Calandrella raytal
ORIENTAL SKYLARK Alauda gulgula
PLAIN FLOWERPECKER Dicaeum concolor
142
C. INSKIPP and T. P. INSKIPP
Forktail 9
RED-HEADED BULLFINCH Pyrrhula erythrocephala
WHITE- WINGED GROSBEAK Mycerobas carnipes
GOLD-NAPED FINCH Pyrrhoplectes epaulena
CRESTED BUNTING Melophus lathami
LITTLE BUNTING Emberiza pusilla
BLACK-FACED BUNTING Emberiza spodocephala
Key
1st trek
T = Tropical zone
S = Subtropical zone
P = Temperate zone broadleaved forest
Both treks
F = Fields, grazing areas and around human habitation
R = Rivers and lakes
2nd trek
U = Subtropical zone broadleaved forest
B = Temperate zone broadleaved forest
X = Temperate zone mixed forest
C = Temperate zone coniferous forest
H = Subtropical zone Chir Pine forest
Locations:
1 Paro (2,250 m) - Thimphu (2,400 m)
2 Thimphu valley (2,400 m)
3 Tseri (2,500 m - 2,600 m)
4 Thimphu (2,400 m) - Phuntsholing (350 m)
5 Phuntsholing (350 m)
6 Royal Manas National Park (250 m - 550 m)
7 Manas (550 m) - Dalim (710 m)
8 Dalim (710 m) - Tshobrang (1,395 m)
9 Tshobrang (1,395 m) - 1,615 m - Ponchela (1,400 m)
10 Ponchela (1,400 m) - 2,390 m - Subrang (1,400 m)
1 1 Subrang (1,400 m) - 1,525 m - Zurphey (1,320 m)
1 2 Zurphey ( 1 ,320 m) - Tshanglajong ( 1 ,065 m)
1 3 Tshanglajong ( 1 ,065 m) - Tingtibi (650 m)
14 Tingtibi (650 m - 810 m)
15 Tingtibi (650 m) - Tongsa (2,200 m)
16 Tongsa (2,200 m)
17 Chendibji (2,400 m)
1 8 Pele La (2,930 m - 3,2 1 0 m)
1 9 Phobjikha valley (2,780 m - 2,870 m)
20 Phobjikha (2,780 m) - Khebatang (2,800 m)
21 Khebatang (2,800 m) - Gele La (3,630 m) - Laphu Gang (3,100 m)
22 Laphu Gang (3,100 m) - Pema La (3,290 m) - Nehi (2,440 m)
23 Nehi (2,440 m)
24 Nehi (2,440 m) - Harachhu (1,125 m)
25 Harachhu (1,125 m - 1,445 m)
26 Harachhu (1,125 m) - 1,695 m - Nashina (1,220 m)
27 Nashina (1,220 m)
28 Nashina (1,220 m) - 1,435 m - Ada (1,280 m)
29 Ada (1,280 m)
30 Ada (1 ,280 m) - Tarana (2,430 m)
31 Tarana (2,430 m) - Phobjikha (2,780 m)
32 Phobjikha (2,780 m) - Thimphu (2,400 m)
33 Tashigong monastery/Dochu La (2,840 m - 3,530 m)
1994
SHORT COMMUNICATIONS
143
The birds of Pakistan: supplementary
observations from the northern Punjab
and hills
A. VITTERY
I was resident in Lahore from May 1973 to early June 1974. Some of my
observations in the first part of this period were included by T. J. Roberts in
The birds of Pakistan (1991 and 1992) but other data appear never to have
reached him. The following accounts are limited to those species where my
records add materially to the status described by Roberts. These include an
addition to the Pakistan list: Richard’s Pipit Anthus richardi ; one probable
addition: Blyth’s Pipit A. godlewskii. ; three revised first records for Pakistan:
Pied Harrier Circus melanoleucos, Brown Crake Amauromis akool and Mew
Gull Larus canus; four first inland occurrences of migratory waders and the
first inland and autumn records ofWhite-winged Tern Chlidonias leucopterus.
ALPINE SWIFT Tachymarptis melba In 1973 a total of 14 flew north/north¬
east over Lahore on 24 July, one flew south-west at Balloki, 64 km south-west
of Lahore on 26 July, and two flew north over Lahore on 28 August.
PALE-BACKED PIGEON Columba eversmanni Two flocks totalling 75
birds were seen in an arid area near Raiwind on 2 February 1974, and nine
beside the Hudiara drain, south-west of Lahore, on 26 February 1974. It
does not seem to have been recorded in the northern foothills but there were
10 near Rawal Lake, Islamabad, on 16/17 February 1974.
BROWN CRAKE Amauromis akool One was well seen at the Balloki
headworks on 20 January 1974 and there were two there on 3 March 1974
(one of which caught and ate a mud-skipper). These predate the only record
listed by Roberts.
RUDDY-BREASTED CRAKE Porzanafusca Seen at the Balloki headworks
on six dates between 3 February and 26 May 1973, max. 6+ on 10 March.
Considered rare to scarce by Roberts, who also saw one at Balloki, on 28
March 1981.
BLACK-TAILED GODWIT Limosa limosa According to Roberts, ‘seldom
encountered’ in the Punjab. There were two at Kharrar jheel, near Renala
Khurd, on 21 July 1973, two on 7 October 1973 and one on 19 May 1974.
WHIMBREL Numenius phaeopus Roberts knew of no inland occurrences.
There was one on the River Ravi at Niaz Beg, Lahore, on 27 September 1973
and two at Kharrar jheel on 7 October 1973. The call was heard on both
occasions.
144
SHORT COMMUNICATIONS
Forktail 9
COMMON REDSHANK Tringa totanus Earliest near Lahore on 12 July
1973 and at least 50 at Ivharrar jheel by 21 July (earliest date cited by
Roberts).
MARSH SANDPIPER Tringa stagnatilis A notable count of 1,140 at
Kharrar jheel on 2 1 July 1973. There were still at least 300 there on 7 October
1973andaflockof80eastofBahawalnagaron 1 April 1974. Latest were nine
at Kharrar jheel on 19 May 1974.
COMMON GREENSHANK Tringa nebularia Earliest near Lahore 12 July
1973 with flocks of 1 1 on 15 July and 28 on 24 July.
GREEN SANDPIPER Tringa ochropus The late June birds thought by
Roberts to be summering would almost certainly be returning migrants, since
this species is known to leave the breeding grounds from early June. In 1973
birds were widespread in the Lahore area by 3 July.
WOOD SANDPIPER Tringa glareola Earliest near Lahore 12 July 1973.
Latest (two or three) at Kharrar jheel on 19 May 1974.
TEREK SANDPIPER Tringa cinerea Roberts cites only one inland
occurrence. I saw this species on three dates in the Lahore area: three near
Raiwind and one at Julke on 14 September 1973, 4 (flew south-east) at Niaz
Beg on the River Ravi on 27 September 1973 and one at Balloki headworks
on 26 May 1974.
COMMON SANDPIPER Tringa hypoleucos Earliest were 6 near Lahore on
15 July 1973. Latest on 17 May 1974.
RUDDY TURNSTONE Arenaria inteipres Roberts knew of no inland
occurrences. There was one at Kharrar jheel on 19 May 1974.
SANDERLING Calidris alba Neither Roberts nor Ali and Ripley (1969)
knew of inland occurrences in the subcontinent. On 12 August 1973, three
flew low over floodwater at Balloki but left to the north-east without landing.
There was also one near Raiwind from 30 September - 2 October 1973.
TEMMINCK’S STINT Calidris temminckii Roberts cites arrivals from mid-
August. In 1973 small numbers appeared around Lahore in late July (earliest
21st).
SHARP-TAILED SANDPIPER Calidris acuminata Roberts credits me in
error with a sighting at Kharrar jheel in 1970. My only encounter with Sharp¬
tailed/Pectoral Sandpipers was on 21 September 1973 when a party of four
was flushed from floodwater beside the main Multan road to the south-west
of Lahore. Their low ‘trrrt - trrrt’ calls sounded more like Pectoral Sandpiper
C. melanotos than Sharp-tailed, but I was unable to confirm the identification.
DUNLIN Calidris alpina Earliest was one at Ivharrar jheel on 21 July 1973.
CURLEW SANDPIPER Calidris ferruginea Earliest were eight at Kharrar
jheel on 21 July 1973. At least 50 there on 19 May 1974.
BROAD-BILLED SANDPIPER Limicola falcinellus Roberts cites only one
inland occurrence. There was one at Kharrar jheel on 19 May 1974.
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BLACK- WINGED STILT Hirnantopus himantopusNotab\e counts of2,000+
at Kharrarjheel on 7 October 1973, and at least 4,000 there on 19 May 1974.
PACIFIC GOLDEN PLOVER Pluvialis fulva Roberts noted that it is rarely
encountered far from the sea-coast. There were nine near Raiwind on 30
September 1973 (with four remaining until 4 October) and three at Kharrar
jheel on 19 May 1974.
COMMON RINGED PLOVER Charadrius hiaticula One was seen and
heard near Raiwind, south of Lahore, on 4 January 1974 and another was
heard at Kharrar jheel on 17 March 1974. These represent the first inland
records.
COLLARED PRATINCOLE Glareola pratincola Roberts describes this
species as a “rare straggler” in the Punjab and gives 1 7 September as the latest
date. I saw it frequently south of Lahore from 5 May to 7 October, maxima
of 20 at Kharrar jheel (including a newly fledged juvenile) on 21 July 1973,
at least 1 00 at Balloki headworks on 26 July 1 973 and up to 35 at each of three
localities in August 1973.
INDIAN SKIMMER Rynchops albicollis Roberts knew of no recent winter
records. There was one at the Wahdat ponds on the western outskirts of
Lahore on 27 December 1973.
MEW GULL Lams canus Roberts mistakenly gives the first record of this
species from the Ravi River near Lahore in 1 972. In fact, the first record (for
the subcontinent) was of an adult at the Rasul barrage on 27 January 1974
seen by F. J. Koning, L. J. Djiksen and myself. On 17 February 1974 there
was a first winter bird on Rawal Lake, Islamabad.
WHITE-WINGED TERN Chlidonias leucopterus Roberts describes this
species as a rare spring passage migrant, first recorded as recently as 1970.
In the Lahore area I saw it on three occasions in autumn 1973 (none in
spring) : an adult moulting into winter plumage near Julke on 1 4 September,
a flock of 1 2 juveniles nearby at Raiwind on 30 September and five at the same
locality on 2 October (probably part of the same flock). There was also a
juvenile at Khabbaki Lake (Salt Range) on 21 October.
PIED HARRIER Circus melanoleucos Roberts cites only one record
(December/January 1985/1986). During an exceptionally cold spell a male
was quartering fields on the south-west outskirts of Lahore on 27 December
1973. This adds greater credence to the undated record of a bird “putatively
seen” at Lahore by A. J. Currie in the 1920s (Ali and Ripley 1968) which
Roberts overlooks (or discounts).
BLACK BITTERN Ixobrychus flavicollis Two at Balloki headworks from 8
July - 5 August 1973 and on 28 April 1974.
DARK-THROATED THRUSH Turdus mficollis A male of the red-throated
race mficollis (but not dull maroon-chestnut as described by Roberts) was
seen near the Balloki headworks on 3 March 1974.
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SLATY-BLUE FLYCATCHER Ficedula tricolor A male in the Jinnah
Gardens, Lahore, on 1 3 February 1 974 seems to be the first record away from
the foothills.
COMMON GRASSHOPPER-WARBLER Locustella naevia Roberts noted
that it was apparently scarce, with records from only four observers. One near
Lai Suhanra on 30 March 1974.
MOUNTAIN CHIFFCHAFF Phylloscopus sindianus The status of this
species between its breeding and wintering grounds is obscure. In the Lahore
area in 1974 there was a marked spring passage from 3 March to 1 1 April,
with small numbers seen in ten localities. Further south, in late March larger
numbers were seen around Lai Suhanra and Fort Abbas, max. 20+ at the
former on 29/30 March. Two were in song at Balloki on 17 March.
BLYTH'S LEAF-WARBLER Phylloscopus reguloides Roberts knew of no
records outside of the breeding season, although he states that the species
‘migrates in winter to the foothills and adjacent plains’. On 2 1 October 1 973
there was one in the Bakh Hund pass between Naushara and Nurewala (Salt
Range) - a rather small crown-striped warbler with two conspicuous yellow
wing-bars, yellowish-white supercilia and white in the outer tail-feathers.
LARGE GREY BABBLER Turdoides malcolmi Roberts recorded it as a rare
resident, with only three records in the last 80 years. I saw this species four
times by the River Ravi at Niaz Beg, Lahore, between 1 1 September 1973
and 24 January 1974, max. five on 8 January 1974. Further north, there was
one east of Shekupura on 20 October 1973.
RUFOUS-TAILED LARK Ammomanes phoenicurus Roberts knew of no
recent occurrences. My two sightings fit the ‘monsoon’ pattern of Waite’s
earlier records: one flew NE at Balloki on 26 July 1973 and one flew SE at
Niaz Beg on the River Ravi, Lahore, on 13 September 1973.
EURASIAN TREE SPARROW Passer montanus Roberts states that in
Pakistan it is confined to the drier mountain regions of the west. A small flock
near Sakesar (Salt Range) on 21 October 1973 was outside of this range.
RICHARD’S PIPIT Anthus richardi Roberts included this, and the Paddyfield
Pipit A. rufulus, in A novaeseelandiae but makes no mention of the occurrence
of richardi. On 1 6 September 1973a large, dark, long-tailed pipit flew W near
Raiwind, giving the characteristic ‘dzreeep’ call of richardi. Another was seen
at Niaz Beg on the River Ravi on 20 September 1973.
BLYTH’S PIPIT Anthus godlewskii Roberts makes no reference to this
species, although Vaurie (1959) includes Pakistan in its winter range, and
one of the known Indian wintering areas is not far to the south-east of Sind
(Ali and Ripley 1973). On 13 September 1973 I had close views of a pipit at
Niaz Beg, Lahore, which was larger than A. rufulus waitei but smaller and
shorter-tailed than A. richardi. It had warm buff underparts, richer on the
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flanks and paler on the rather finely streaked breast. The brown back was
almost as dark as that of A. richardi but the pattern on the median and greater
coverts resembled that ol Tawny Pipit A. campestris. The harsh ‘p-titt’ call
was unfamiliar but does not seem to correspond closely to calls so far
attributed to A. godlezvskii. There was a similarly plumaged (but silent) bird
at the same locality on 9 October 1 973. At the time no good field descriptions
of A. godlezvskii existed but, on the basis of information now available, it
seems these birds were probably of this species.
RED-THROATED PIPIT Anthus cervinus Three additional winter records
of two by the Hudiara drain on 26 December 1973, two on the south-west
outskirts of Lahore on 27 December 1973 and two at Kharrar jheel on 10
February 1974 suggest that the species is thinly distributed in the northern
Punjab. However, the exceptionally cold weather of late December 1973
may have induced movement from elsewhere.
ROSY PIPIT Anthus roseatus I found this to be a rather more common winter
visitor (late December to March) in the northern Punjab than Roberts
suggests. It was quite widespread on the fringes of lakes, marshes and ditches
with maxima of 1 2 at Kharrar jheel on 3 1 December 1973, nine near Raiwind
on 2 February 1974 and 5 at Balloki on 3 March 1974.
SPECTACLED FINCH Callacanthis burtoni An unusually large flock of 40
was seen at just over 2,000 m near Murree on 1 6 February 1 974. There was
also one at Nathia Gali on 15 April 1974.
PINK-BROWED ROSEFINCH Carpodacus rodochrous Roberts regarded it
as scarce. A male was seen above Ghora Gali on 1 6 February 1974 and there
were two females in the same area on 13 April 1974 plus at least six (three
males) at Nathia Gali on 15 April 1974.
REFERENCES
Ali, S. and Ripley, S. D. (1968) Handbook of the birds of India and Pakistan, 1 . Bombay: Oxford University
Press.
Ali, S. and Ripley, S. D. (1969) Handbook of the birds of India and Pakistan, 2. Bombay: Oxford University
Press.
Ali, S. and Ripley, S. D. (1973) Handbook of the birds of India and Pakistan, 9. Bombay: Oxford University
Press.
Roberts, T. J. (1991-1992) The birds of Pakistan. Two vols. Karachi: Oxford University Press.
Vaurie, C. (1959) The birds of the Palearctic fauna, Passeriformes. London: Witherby.
Alan Vittery, 164 West Clyne, Brora, Sutherland KW9 6NH, U.K.
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Observations on the breeding of the
Palawan Blue-Flycatcher Cyornis
lemprievi
D. G. VRETTOS
The Palawan Blue-Flycatcher Cyornis lemprien 'is a Philippine endemic which
has been treated either as a subspecies of the Hill Blue-Flycatcher C.
banyumas (Watson et al. 1986), or as a full species (Dickinson et al. 1991).
DESCRIPTION AND MEASUREMENTS
Previously published descriptions of this species are incomplete and, therefore,
full details are provided:
Male: forehead light blue; crown, nape, back, wings, mantle, sides of head,
ear-coverts and rump dark blue; lores black; chin off-white, changing to pale
orange on the breast; belly white; under tail-coverts off-white; flanks and
under wing-coverts grey; tail dark blue; eye dark brown; legs blue-grey; bill
black.
Female: crown and nape blue-grey; lores black; white supercilium and
malar stripe; ear-coverts greenish-grey; back, mantle and rump olive-brown;
tail rufous-brown; chin white, changing to dull orange on the breast; belly
white; under tail-coverts and under wing-coverts off-white; wings and flanks
dark brown; eye dark brown; legs blue-grey; bill black.
The average measurements of three males caught in mist nets at the end
of July were: wing 79 mm, tail 63.3 mm, bill 15.3 mm, tarsus 21 .3 and weight
22.062 g. One of the males netted on 27 July was in moult. Two females
caught at the same time averaged: wing 77 mm, tail 58 mm, bill 1 5 mm, tarsus
21 mm, weight 21.2 g.
BREEDING BEHAVIOUR
Observations on the breeding of this flycatcher began on the 14 April 1987
when, what was thought to be an old empty nest was found, in a hollow tree-
stump, by members of the Palawan Wildlife Expedition. The team was mist-
netting on the east slope of Mount Mananangob (9°46’N 1 18°41’E), in the
central mountain range of the island, at an altitude of approximately 370 m.
Mount Mananangob is in a watershed reserve near the village of Irawan,
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which is 1 1 km from Puerto Princesa city on the southbound road.
There is a limited amount of disturbance from illegal logging, hunting by
villagers, and also collecting of honey. Resin from the Almaciga tree Agathis
dammara is collected seasonally by the Tagbanuwa people, who employ a
system of shifting cultivation.
The following day (15 April) an egg was discovered in the nest, and an
observation hide was therefore constructed from fish-tail palm Arenga
fronds, between the buttress roots of a large tree which was about 3 m from
the nest site. The nest, which was constructed from dried grasses, and
measured 50 mm deep by 60 mm inside diameter, was not visible from the
hide as it was set back in the 1 m high stump.
Early the next morning (16 April) I took up position in the hide and settled
down to wait. About 15m from the hide was a stream which ran down the
hillside and, since it was still the dry season, this was visited by a variety of
birds and mammals. Some of these, such as Crab-eating Macaque Macaca
fascicularis, Sunda Civet Viverra tangalunga. Common Palm Civet Paradoxurus
hermaphroditus , Palawan Treeshrew Tupaia palawanensis and Palawan Hombill
Anthracoceros marchei, were potential predators. Just after midday a small
brown passerine appeared on a nearby branch and then flew into the nest.
This was later identified as a female Palawan Blue-Flycatcher.
The Mangrove Blue-Flycatcher C. rufigastra occurs in that area of Palawan,
and the male is very similar to that of the Palawan Blue-Flycatcher; however,
the female rufigastra is mainly blue like the male, whereas the female lemprieri
is brown. Both adult Palawan Blue-Flycatchers were seen together on
numerous occasions, facilitating positive identification of the species.
On checking the nest in the late afternoon it was noted that there was still
only one egg.
At 06h00 the next morning ( 1 7 April) I again settled down in the hide. The
female appeared about 20 minutes later and flew to the nest. During
subsequent observations it was not always possible to be sure that the female
was sitting because her approaches and departures were very rapid . Later that
day a snake, possibly a cobra Naja, about 2.5 m long, passed the nest site at
about 2 m distance. At 1 7h00 I left the hide and found that a second egg had
been laid when I checked the nest.
The following day (18 April) the male Palawan Blue-Flycatcher was seen
for the first time. It appeared on a branch about 2 m from the nest, and then
chased off a male Blue-and-white Flycatcher Cyanoptila cyanomelana which
came close to the nest. Later that day both the adults mobbed two juvenile
Palawan Tree-shrews which wandered close to the nest. The female left the
nest several times to feed. At 17h00 there were still two eggs in the nest.
The next day (19 April) it quickly became apparent that the birds were
uneasy because the hide no longer provided adequate concealment. The hide
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Forktail 9
was abandoned but the nest was subsequently checked every 2-3 days. On 2 1
April a check revealed that the female was temporarily absent and the
opportunity was taken to measure the eggs. One was 24x 1 6 mm and the other
was 22.5x15.5 mm. They were pale blue and with reddish-brown blotches
concentrated towards the blunt end.
Two chicks were discovered in the nest on 2 May. The nest had been
checked on 30 April with no sign of the eggs hatching, giving an incubation
period of 1 5- 1 6 days, assuming that the second egg was laid on 1 7 April and
that incubation started then.
The hide was hastily repaired on 3 May and observations were resumed at
05h30 on 4 May. Both parents made frequent visits to the nest, but as they
flew directly into the nest it was difficult to see what food they were carrying.
Feeding took only 3-4 seconds each time and the adults collected most of the
food close to the nest. The female spent several periods of about 30 mins in
the nest, presumably brooding the young. Over the next four days the
frequency of feeding increased but on the morning of 9 May both young had
disappeared. Both adults were still in the area but there was no sign of any
fledglings.
Many thanks to Mr R. P. Girdler for his comments on the manuscript.
REFERENCES
Dickinson, E. C., Kennedy, R. S. and Parkes, K. C. (1991) The birds of the Philippines. Tring: British
Ornithologists’ Union (Check-list no. 12).
Watson, G.E., Traylor, M. A. and Mayr, E. (1986) Muscicapidae. Pp. 295-375 in E. Mayr and G. W.
Cottrell, eds., Check-list of birds of the world, 1 1 . Cambridge, Massachusetts: Museum of Comparative
Zoology.
Dennis G. Vrettos, Basil Comer, Lower Basildon, Berkshire, RG8 9NL, U.K.
Blyth’s Leaf- Warbler Phyllo scopus
reguloides found breeding in Thailand
PER ALSTROM and URBAN OLSSON
This note describes the first confirmed breeding of Blyth’s Leaf-Warbler
Phylloscopus reguloides in Thailand, namely at Doi Inthanon in the north¬
west. It is suggested that Blyth’s Leaf-Warbler is breeding rather commonly
on Doi Inthanon, and that it has been overlooked before.
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In early April 1991 P.A. observed several Blyth’s Leaf-Warblers on the
summit of Doi Inthanon, north-west Thailand (18°35’N 98°29.5’E). Some
of the birds were singing, but it could not be established whether they were
on migration or breeding ( Phylloscopus warblers frequently sing during spring
migration; pers. obs.). In the second week of March 1992 Blyth’s Leaf-
Warbler was found to be locally common on Doi Inthanon, and breeding was
confirmed. This species has not previously been proved to breed in Thailand
(Boonsong et al. 1991; Philip D. Round in litt.).
On 8 March 1992 a pair of Blyth’s Leaf-Warblers were seen nest building,
beside the trail at the summit bog on Doi Inthanon, at an altitude of c. 2,560
m. The following day the nest was abandoned, probably as a result of human
disturbance. On 1 1 March possibly the same pair was seen building a nest
some 30-40 m from the first nest site. On 9 March 1 992 a nest of Blyth’s Leaf-
Warbler with nearly fully grown young was found at c. 1650 m (‘km 37’) on
Doi Inthanon. Two days later the young fledged. On 8 April 1992 Johan
Wallander and Eva Helgesson (pers. comm. 1992) saw a nest-building pair
of Blyth’s Leaf-Warbler near the summit bog on Doi Inthanon.
At the summit of Doi Inthanon, especially in the vicinity of the bog, Blyth’s
Leaf-Warbler was fairly common and outnumbered White-tailed Leaf-
Warbler Phylloscopus davisoni by roughly 2:1 (based on a count of singing
males). At c. 1,650 m (‘km 37’) Blyth’s Leaf-Warbler seemed to be slightly
less numerous than White-tailed Leaf-Warbler, and ate. 1,500 m (‘km 34.5’)
White-tailed appeared to be more numerous than Blyth’s (based on counts
of singing males).
It is quite possible that some or even most of the Blyth’s Leaf-Warblers that
we observed were on migration. This may be supported by the fact that
several singing males did not respond to play-back of their own song.
However, there could be other explanations for that (cf. Alstrom and Olsson
1992). On the other hand, several males (other than those whose nests we
found) were evidently territorial and responded vigorously to play-back, and
at least one of these appeared to have a mate. Even if some of the Blyth’s Leaf-
Warblers that we observed were on migration, it would still appear that
Blyth’s Leaf-Warbler is a fairly common breeding bird on Doi Inthanon.
It may be of some interest to point out that we did not find any Blyth’s Leaf-
Warblers on Doi Suthep-Pui in early March 1992, only White-tailed Leaf-
Warblers.
On plumage (mainly tail pattern) as well as on geographical grounds the
Blyth’s Leaf-Warblers on Doi Inthanon seem to match the subspecies
assamensis. This extension of the known range of Blyth’s Leaf-Warbler
reveals that Blyth’s and White-tailed Leaf-Warblers are sympatric in four
disjunct areas: Doi Inthanon (P. r. assamensis and P. d. davisoni), Sichuan
Province, China (P. r. claudiae and P. d. disturbans ), Fujian Province, China
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Forktail 9
(P. r. fokiensis and P. d. ogilviegranti) and in South Annam, Viet Nam (P. r.
ticehursti and P. d. klossi ) (Watson et al. 1986).
The Blyth’s Leaf-Warblers were distinguished from White-tailed Leaf-
Warbler (of subspecies davisoni , breeding on Doi Inthanon) primarily by (1)
song and calls (also begging calls of juveniles) which were subtly although
consistently different (one species did not respond to play-back of the other
species’ song), (2) tail pattern (Blyth’s showed a narrow white border to the
tip and edge of the inner web of the outermost rectrix, frequently also whitish
mottling centrally on the same feather, although not almost completely white
inner web as in White-tailed; the tail pattern is often extremely difficult to
judge in the field) and (3) antagonistic behaviour (when agitated, Blyth’s has
a distinctive habit of lifting one wing at a time; White-tailed flicks both wings
simultaneously and with a much quicker action than Blyth’s). Also, the
feeding behaviour usually differs significantly between the two species.
Unlike White-tailed, Blyth’s has the characteristic of looking on the undersides
of branches, frequently hanging head-down almost vertically.
It may seem surprising that Blyth’s Leaf-Warbler has been overlooked as
a breeding bird on Doi Inthanon. However, many Blyth’s Leaf-Warblers
have probably routinely been identified as White-tailed Leaf-Warbler, which
is known to breed commonly on Doi Inthanon. Moreover, those visiting
birdwatchers who correctly identified Blyth’s Leaf-Warblers probably did
not bother too much about whether or not they were breeding.
The trip to Thailand was made possible by, in part, a grant from the
Uddenberg-Nordingska Stiftelsen. Thanks also to Phil Round for comments
on this note.
REFERENCES
Alstrom, P. and Olsson, U. (1992) On the taxonomic status of Phylloscopus affinis and Phylloscopus
subaffinis. Bull. Brit. Om. Club 1 12: 111-125.
Boonsong Lekagul, Komolphalin, K., Round, P. D. and Wongkalasin, M. (1991) A guide to the birds of
Thailand. Bangkok: Saha Karn Bhaet.
Watson, G. E., Traylor, M. A., Jr. and Mayr, E. (1986) Family Sylviidae, Old World Warblers. Pp. 3-
294 in E. Mayr and G. W. Cottrell, eds . , Check-list of birds of the World, 1 1 . Cambridge, Massachusetts:
Museum of Comparative Zoology.
Per Alstrom, Kungsgatan 3, 462 33 Vanersborg, Szveden.
Urban Olsson, University of Goteborg, Dept, of Zoology, Section of Morphology
and Systematics, Box 25059, 400 31 Goteborg, Sweden.
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Black Tern Chlidonias niger : a new
species for Sri Lanka
REX I. DE SILVA, ENOKA PERERA, LESTER PERERA and
KANISHKA SAMARASINGHE
On 1 November 1 992, at approximately 1 0h20, we were on the tidal mudflats
in the northern part of Negombo Lagoon (7 9°50’E 7° 1 1 ’N) . A flock of about
60 Whiskered Terns Chlidonias hybridus were perched on a brush-pile fish-
trap about 80 m from us. An unidentified tern was also perched on the trap
in the midst of the Whiskered Terns and was observed through a 20x80
telescope for more than 30 minutes.
The bird was slightly smaller than a Whiskered Tern. Its mantle was brown
and grey, the wings were brownish-grey with darker primaries and a prominent
dark carpal bar. The underparts were white, and the bill, irides and legs were
black. The rump and slightly forked tail were light grey - the rectrix tips being
somewhat darker. Its forehead, chin and neck were white and a cap, which
extended downwards behind the eyes, was present. The cap was dark grey
in front, and sooty-black at the rear, changing to brownish at the edges. A
small diffuse greyish patch was present on each side of the breast below the
closed forewing. The bird preened continuously whilst under observation.
The bird was superficially similar to a juvenile White-winged Tern C.
leucopterus, but the following features served to distinguish it. The grey rump
(i contra white); lack of a prominent saddle effect on the mantle; longer bill;
different cap/head pattern; and the grey patches at the sides of the breast
(always lacking in White-winged Tern).
On reference to Harrison (1985) it was clear that the bird was a juvenile
Black Tern C. niger. This is the first record of the species from Sri Lanka. Six
individuals have been recorded from India, including four at Point Calimere,
Tamil Nadu (Alexander 1950, Abdulali and Ambedkar 1983, Natarajan and
Balasubramian 1991, Menon 1992).
We are grateful to Brindley de Zylva and Kumudini Gomes for commenting
on earlier drafts of the manuscript.
REFERENCES
Abdulali, H. and Ambedkar, V. C. (1983) Occurrence of the Black Tern Chlidonias niger (Linn.) in India.
J. Bombay Nat. Hist. Soc. 80: 640.
Alexander, H.G. (1950) Possible occurrence of the Black Tern Chlidonias niger (L.) near Delhi. J.
Bombay Nat. Hist. Soc. 49: 120.
Harrison, P. (1985) Seabirds: an identification guide. Revised edition. London: Croom Helm.
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Menon, V. (1992) On the Black Tern Chlidonias niger niger (Linn.). J. Bombay Nat. Hist. Soc. 89: 120.
Natarajan, V. and Balasubramian, P. (1991) Additional notes on the occurrence of Black Tern
Chlidonias niger (Linn.) in India. J. Bombay Nat. Hist. Soc. 87: 451-452.
Rex I. De Silva, Hepporawatte, Darnpe, Madapatha, Piliyandala, Sri Lanka
Enoka Perera, 69/3, Green Path, Colombo 7, Sri Lanka
Lester Perera, 34/2, S de S. Jayasinghe, Mawatha, Nugegoda, Sri Lanka
Kanishka Samarasinghe, 2511, Minuwangoda Road, Negombo, Sri Lanka.
Long-billed Plover Charadrius
placidus : a new species for Sri Lanka
REX I. DE SILVA and LESTER PERERA
At about 1 3h00 on 1 0 January 1 993 we were observing birds on the sandspit
at the mouth of the Chilaw Lagoon (79°47’E 7°36’N) in north-west Sri
Lanka. Several species of terns, two Sooty Gulls Lams hemprichi and some
shorebirds were visible. A wader which neither of us could identify, flew
along the shoreline and settled down on the sandspit about 25 m from us.
The bird appeared intermediate in size between a Common Ringed Plover
Charadrius hiaticula and a Greater Sand-Plover C. leschenaultii. The upperparts
were brown and the underparts were white. A greyish-brown breast-band
was present. The crown and lores were the same colour as the upperparts and
there was a light brown supercilium. The forehead was off-white, the chin
and neck were white and there was a white collar. The bill was blackish, the
legs were yellowish-grey, the irides were dark brown and there was a thin, but
prominent, white wing-bar. The bird bore a superficial resemblance to a
Common Ringed Plover in winter plumage, but the noticeably longer legs,
bill and tail served to distinguish it from that species.
The bird was observed for approximately 10 minutes with 8x40 and 8x30
binoculars. On subsequently referring to Hayman et al. (1986) it was
apparent that the bird was a Long-billed Plover C. placidus. This is the first
record of the species for Sri Lanka.
The Long-billed Plover breeds in north-east Asia, and most migrate south
or south-west after breeding, although small resident populations occur in
southern Japan and parts of southern China. It winters from Nepal east to
eastern China and in South Korea and has wandered to Peninsular Malaysia,
Brunei and Bali. However, it has not been recorded previously from south of
22°S in the Indian subcontinent (Thompson et al., this issue).
1994
SHORT COMMUNICATIONS
155
REFERENCES
Hayman, P., Marchant, J. and Prater, T. ( 1 986) Shorebirds: an identification guide to the waders of the world.
London: Christopher Helm.
Rex 1. De Silva, Hepporawatte, Dampe, Madapatha, Piliyandala, Sri Lanka
Lester Perera, 3412, S. de S. Jayasinghe Mawatha, Nugegoda, Sri Lanka.
Asian Stubtail Urosphena squameiceps :
a new species for Nepal and the Indian
subcontinent
ALAN LEWIS
On 2 1 January 1 993 I visited the Dharan forest which lies just north of Itahari
in eastern Nepal. In general the forest was disappointingly quiet but, upon
investigating a slight rustle on the forest floor, I was pleased to find an Asian
Stubtail (Stub-tailed Bush-Warbler) Urosphena squameiceps. It was hopping
jerkily on long, flexed legs in a fashion typical of the genus, and close views
were obtained for about 30 seconds before it disappeared.
The main features noted were the dark brown upperparts, whitish
underparts, very long buffish-white supercilium and a tailless appearance.
The legs and large feet were very pale pink. The views were not sufficient to
see the indistinct scaling on the forehead which is characteristic of the species,
and it was not heard to call.
I am very familiar with Urosphena squameiceps in its wintering areas in
Thailand, and had seen several at Khao Yai National Park less than three
weeks previously.
It was a surprise to discover that this is apparently the first record for Nepal
and the Indian subcontinent. King et al. (1975) give the wintering range in
South-East Asia as ‘Burma (except NE); NW, NE, SE and peninsular
Thailand; NW Tonkin; Laos; Hong Kong.’ It is perhaps to be expected that
a long distance migrant such as the Asian Stubtail, which breeds in north-east
Asia and regularly winters as far west as Myanmar (Burma) , should occasionally
stray further west.
REFERENCES
King, B. F„ Dickinson, E. C. and Woodcock, M. W. (1975) A field guide to the birds of South-East Asia.
London: Collins.
Alan Lewis, 4 Troutbeck Avenue, Congleton, Cheshire CW12 4JA, U.K.
156
SHORT COMMUNICATIONS
Forktail 9
Black- and-yellow Grosbeak Mycerobas
icterioides : a new species for Nepal
ALAN LEWIS
On 22 March 1993 I located a flock of about 100 Collared Grosbeaks
Mycerobas affinis at an elevation of about 3000 m, just below the Deorali
teashop, about 1 V2 hours walk from Ghorepani on the Jomsom trek,
Annapurna Conservation Area, west-central Nepal. They were astonishingly
confiding as they fed on the ground under pine trees, although sections of the
flock would occasionally fly up into the trees when alarmed, but these birds
returned almost immediately.
I walked back to the teashop and met Richard Rowland. On returning to
the flock, I noticed a mid-grey grosbeak Mycerobas with the Collared
Grosbeaks. We watched this bird at close range for about 1 0 minutes, feeding
with the Collared Grosbeaks but also briefly near a male Spectacled Finch
Callacanthis burtoni. The main features noted were the uniform mid-grey
head, mantle and breast, black tail and wings, and a buffish belly and flanks.
There was no perceptible difference in structure or bare part colouration
from the nearby Collared Grosbeaks.
On reference to Ali and Ripley (1983) it was easy to confirm our suspicions
that this bird was a female Black-and-yellow Grosbeak M. icterioides. One
feature not noted, presumably because the wings were held closed, was the
buff rump and uppertail-coverts.
This is the first confirmed record of this species for Nepal, although Inskipp
and Inskipp (1991) mention a previous (probably erroneous) record, which
they place in square brackets. It is also the easternmost record of the species,
apart from that of a specimen collected in Darjeeling, held in the collection
of the Zoological Institute in Leningrad (Neufeldt and Vietinghoff-Scheel
1984).
REFERENCES
Ali, S. and Ripley, S. D. (1983) A pictorial guide to the birds of the Indian subcontinent. Bombay: Oxford
University Press.
Inskipp, C. and Inskipp, T. (1991) A guide to the birds of Nepal. Second edition. London: Christopher
Helm.
Neufeldt, I. A. and Vietinghoff-Scheel, E. v. (1984) Mycerobas icterioides (Vigors). In H. Dathe and I.
A. Neufeldt, eds., Atlas der Verbreitung Palaearktischer Vogel, 12. Berlin: Akademie-Verlag.
Alan Lewis, 4 Troutbeck Avenue, Congleton, Cheshire CW12 4 JA, U.K.
1994
SHORT COMMUNICATIONS
157
Oriental Honey-buzzard Pernis
ptilorhyncus : a new species for the
Andaman Islands
VIBHU PRAKASH, NIKITA V. PRAKASH and
WILLIAM S. CLARK
While conducting surveys for diurnal raptors on the Andaman Islands, we
sighted and identified four juvenile Oriental Honey-buzzards Pernis
ptilorhyncus , apparently the first records of this species for these islands. Ali
and Ripley (1978) do not mention these islands in the species’s distribution,
nor did Abdulali (1964, 1967) collect or report observing this species during
his collecting expeditions there. Finally, Tikader ( 1984) does not include the
Oriental Honey-buzzard in the list of birds for these islands.
On 1 6 February 1 983 at Kalighat on North Andaman Island, we saw three
juvenile Oriental Honey-buzzards begin to soar about 09h00. The next day,
at about 09h00, we saw a single juvenile of this species soaring on the very
eastern slopes near Saddle Peak, also on North Andaman Island.
All four birds were identified by their wing and tail shape and long narrow
necks (Clark and Schmitt 1992). All of us are extremely familiar with this
species from numerous sightings in all parts of India. All the individuals
observed in the Andamans were judged to be juveniles by their darker
secondaries that contrasted with paler primaries when viewed from below,
and by the dark on the outer primaries extending from the tips inward beyond
the feather emarginations (Clark and Schmitt 1992), as confirmed by
photographs taken of three of these individuals. One of the three birds seen
on 1 6 February was a dark morph; the others were light morph individuals.
We do not feel confident to judge the race of these individuals in the field
and, therefore, it was not possible to determine whether these birds were
migrants from north-east Asia on their wintering grounds (P. p. orientalis ), or
were the offspring of local breeding birds or short distance migrants from
mainland India or Myanmar (P. p. ruficollis). Vaurie and Amadon (1962)
discuss the races and status of this species.
This research was conducted by the Bombay Natural History Society as
part of its birds of prey survey project. Clark’s visit to India was supported
by the U.S. Fish & Wildlife Service. D. Ferguson is thanked for his support
of this project.
REFERENCES
Abdulali, H. (1964) The birds of the Andaman and Nicobar Islands. J. Bombay Nat. Hist. Soc. 61: 483-
571.
Abdulali, H. (1967) The birds of the Nicobar Islands, with notes on some Andaman birds. J. Bombay
Nat. Hist. Soc. 64: 139-190.
158
SHORT COMMUNICATIONS
Forktail 9
Ali, S. and Ripley, S. D. (1987) Compact edition of the handbook of the birds of India and Pakistan. Delhi:
Oxford University Press.
Clark, W. S. and Schmitt, N. J. (1992) Flight identification of Indian raptors with pale bars on upper
wings. J. Bombay Nat. Hist. Soc. 89: 1-3.
Tikader, B. K. (1984) The birds of the Andaman and Nicobar Islands. Calcutta: Zoological Survey of India.
Vaurie, C. and Amadon, D. (1962) Notes on the honey buzzards of eastern Asia. Atner. Mus. Novital.
2111.
Vibhu Prakash and Nikita V. Prakash, Bombay Natural History Society, Hombill House, Shaheed Bhagat
Singh Road, Bombay 400 023, India
William S. Clark, 4554 Shetland Green Road, Alexandria, VA 22312, U.S.A.
Golden-spectacled Warbler Seicercus
burkii : a new species for Malaysia
RICHARD GREGORY-SMITH
A Golden-spectacled Warbler Seicercus burkii was netted and photographed
at Sintok on 1 3 October 1991. Sintok is north of Alor Setar, and just below
the Kedah-Thai border. Mist-nets were erected in an area of semi-evergreen
rain-forest with some bamboo.
The nets were inspected at 09h50 and the warbler was found together with
a Siberian Blue Robin Luscinia cyane and a Yellow-breasted Flowerpecker
Pnonochilus maculatus. The warbler weighed 9.5 g and its dimensions were:
overall length 1 1 2 mm, wing 58 mm and tarsus 22 mm. It had a single yellow
wing-bar and conformed in all respects with the description in King et al.
(1975). A photograph was sent to Dr David Wells at the University of
Malaya, who confirmed the identification.
Boonsong and Round (1991) refer to the Golden-spectacled Warbler as a
common winter visitor and passage migrant in Thailand, and indicate that
its range does not extend into the peninsula south of about 10°N. Smythies
(1986) refers to the species as a winter visitor/altitudinal migrant in Myanmar
(Burma), not recorded south of Amherst District in Tenasserim.
The capture of this species in Peninsular Malaysia shows a considerable
extension to its range, and adds a new species to the avifauna of that country.
REFERENCES
Boonsong Lekagul and Round, P. D. (1991) A guide to the birds of Thailand. Bangkok: Saha Karn Bhaet.
King, B. F., Dickinson, E. C. and Woodcock, M. W. (1975) A field guide to the birds of South-East Asia.
London: Collins.
Smythies, B. E. (1986) The birds of Burma. Liss, U.K.: Nimrod Press.
R. Gregory-Smith, Universiti Malaysia Sarawak, 94300 Kota Samarahan, Sarawak, East Malaysia
1994
159
Guidelines for contributors
Forktail publishes original papers in the English language (also, in certain cases, English translations of
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west, Lydekker’s Line to the east (i.e. the eastern boundary of Wallacea), the Chang Jiang (Yangtze
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Forktail 9
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suggest...’. More than one within the same parentheses should be chronologically listed, alphabetically
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etc., after the date. Full references must be listed alphabetically at the end in the form:
Campbell, B. and Lack, E. eds. (1985)^4 dictionary of birds. Calton (Staffordshire, U.K.): T. and A. D.
Poyser.
King, B. F., Dickinson, E. C. and Woodcock, M. W. ( 1975) A field guide to the birds of South-East Asia.
London: Collins.
Kuroda, Nh., ed. (1984) Ketteiban seibutsu daizukan; chorui [ Illustrations of animals and plants: birds],
Tokyo: Sekai Bunkasha. (In Japanese.)
Roslyakov, G. E. (1985) [‘Information on the distribution and number of Aix galericulata and Mergus
squamatus over Khabarovsk Territory.’] Pp. 101-102 in N. M. Litvinenko, ed. Rare and endangered
birds of the Far East. Vladivostok: Far East Science Center, Academy of Sciences of the USSR. (In
Russian.)
Sien Yao-hua, Kuan Kuan-Hsiin and Zheng Zuo-xin (1964) [‘An avifaunal survey of the Chinghai
province.’] Acta Zool. Sinica 16: 690-709. (In Chinese.)
Smythies, B. E. (198 1) The birds of Borneo. Third edition. Kota Kinabalu and Kuala Lumpur: The Sabah
Society and the Malayan Nature Society.
Somadikarta, S. (1986) Collocalia linchi Horsfield & Moore - a revision. Bull. Brit. Om. Club 106: 32-
40.
White, C. M. N. and Bruce, M. D. (1986) The birds of Wallacea (Sulawesi, the Moluccas and Lesser Sunda
Islands, Indonesia): an annotated check-list. London: British Ornithologists’ Union (Check-list no. 7).
It will be noted from these examples that references to non-Roman scripts need to be transliterated
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ISSN 0950-1746
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Cover photograph: Red-tailed Tropicbird Phaethon rubricauda. Photo: Anders Tyevad/Biofoto
CONTENTS
J. S. ASH and A. SHAFEEG.
The birds of die Maldives . 3
A. PRIEME and B. OKSNEBJERG.
The avifauna and conservation value of Shey-Phoksundo National Park, Nepal . 33
D. N. KURUP and V. J. ZACHARIAS.
Birds of Lakshadweep Islands, India . 49
P. SINGH.
Recent bird records from Arunachal Pradesh, India . 65
S. PANDEY, J. JOSHUA, N. D. RAI, D. MOHAN, G. S. RAW AT,
K. SANKAR, M. V. KATTI, D. V. S. KHATI and A. J. T. JOHNSINGH.
Birds of Rajaji National Park, India . 105
R. SANKARAN.
Ornithological survey of Nanda Devi National Park, India . 1 15
A. ROBERTSON.
Occurrence of some pelagic seabirds (Procellariiformes) in waters off
the Indian subcontinent .
J. C. EAMES, C. R. ROBSON and NGUYEN CU.
A new subspecies of Spectacled Fulvetta Alcippe ruficapilla from Vietnam . 141
P. D. ROUND and V. LOSKOT.
A reappraisal of the taxonomy of the Spotted Bush-Warbler Bradypierus thoracicus . 159
Short communications
W. S. CLARK and A. A. KHAN.
Sightings of two rare raptors, Lesser Spotted Eagle Aquila pomarina and
Pied Harrier Circus melanoleucos, in Pakistan .
R. DRIJVERS.
Horned Grebe Podiceps auritus: a new species for India .
O. F. JAKOBSEN.
Red-tailed Tropicbird Phaethon rubricauda : a new species for Thailand .
O. F. JAKOBSEN.
Eyebrowed Thrush Turdus obscurus: a new species for Sri Lanka .
G. FINCH and M. KENNEWELL.
Japanese Thrush Turdus cardis: a new species for Thailand .
G. CLARK.
Rosy Starling Stumus roseus at Khao Sam Roi Yot: a new species for Thailand
H. A. FORD.
Plain Sunbird Anthreptes simplex feeding on arils of acacia seeds .
S. J. M. BLABER and D. A. MILTON.
The distribution of nests of the Black-and-red Broadbill
Cymbirhynchus macrorhynchus along a river in Sarawak .
G. E. MORRIS.
Mountain Hawk-Eagles Spizaetus nipalensis in Vietnam .
Index to Forktails 1-9 .
173
175
177
178
179
180
181
182
184
186
Guidelines for contributors
192
2
Forktail 10
ISSN 0950-1746
© Oriental Bird Club 1994
Published for the Oriental Bird Club by
Rubythroat Publications
6 Corinthian Close, Basingstoke
Hampshire RG22 4TN U.K.
Printed on recycled paper by GL Print, Aldermaston, U.K.
1994
FORKTAIL 10 (1994): 3 - 32
3
Birds of the Maidive Islands, Indian
Ocean
J. S. ASH and ALI SHAFEEG
An annotated checklist of the birds of the Maidive Islands, Indian Ocean, includes 147 species, of
which details of 35 additions are included. New information has resulted principally from field
observations in 1 984 and 1 993, and from an examination of a collection of bird photographs formed
by Mr Ahamed Shafeeg. The White-eyed Gull Larus leucophthalmus is new for the Oriental Region.
The main purposes of this paper are threefold: first, to present an updated
annotated checklist for the birds of the Maldives; second, to report the
occurrence of many new species to the Maldives resulting from an examination
of a large series of photographs collected by Mr Ahamed Shafeeg (father of
A. S.) ofbirds captured in the Maldives and brought alive to Male; and third,
to record observations made on two visits by J. S. A. in 1984 and 1993.
The background to the ornithology of the Maldives has been given by
Phillips (1963), together with a detailed description of the geography and
ecology of the archipelago, so that it is unnecessary to repeat it here. One
point emphasised by Phillips was that relatively few observations had been
made on the Maldives prior to his visit, and after 1963 there was no
improvement. A temporary flush of observations resulted from personnel
working at the British base on Gamu (Seenu Atoll), and the recent upsurge
in tourism will inevitably result in an increase in observers.
A number of factors have changed in the Maldives, mostly to the
detriment of both resident and visiting birds. Perhaps the most important
of these is the development of tourism resulting in a major ecological impact
on an increasing number of islands; an increase in the amount of boat traffic
and movement of people within the archipelago, resulting in increased
disturbance to previously little visited islands; and an increase in affluence,
with its concomitant increase in leisure time, resulting in yet more persecution
ofbirds and the means to obtain them. Unfortunately, persecution ofbirds
has always been intense in the Maldives, but this is apparently now made
worse by the rapidly increasing human population, currently with an annual
growth rate of 3.4%, combined with a major reduction in infantile mortality.
In the past the harvesting of eggs and chicks as food presumably took place
to supplement the otherwise unvarying diet of fish as animal protein.
Keeping a wide range of species of captured birds as pets and toys has long
been, and still is, a very popular pastime in the Maldives. Presumably there
has been severe deforestation of the Maldives in the past, as on the Chagos
Archipelago (Bourne 1971), but it is regrettable to see that it still continues
where trees remain.
4
J. S. ASH and ALI SHAFEEG
Forktail 10
The government’s earlier policy to eliminate the endemic subspecies of
the House Crow Corvus splendens maledivicus, which is very often a pest,
would, if successful, inevitably have resulted in the elimination of its avian
parasite, the Asian Koel Eudynamys scolopacea. However, the crow’s
absence could have a beneficial effect in permitting many other species to
spread and breed successfully (e.g. the Common White-Tern Gygis alba),
and also on allowing visiting raptors to remain and exert some measure of
control over other troublesome pests such as House Rats Rattus rattus and
Indian Flying-foxes Pteropus giganteus. The Ministry of Fisheries and
Agriculture’s policy now is to contain the crow’s population within acceptable
numbers. No doubt a large measure of crow control could be obtained by
reducing the amount of food made available to them in terms of human food
remains and fish garbage, together with an improvement in sanitary
conditions. A certain amount of nest destruction might also be carried out
at critical periods in the breeding cycle.
Under the present system, where tourism is being encouraged (e.g. the
number of islands set aside as tourist resorts has increased from four in 1974
to 70 in 1994), the development of wildlife as an added attraction could be
of great importance - as has been demonstrated in so many other countries.
Following the visit in 1 993 recommendations were made to the government
(Appendix 3) suggesting that a conservation-oriented policy of habitat and
wildlife protection could be developed, with one object being the increase
of large colonies of seabirds. Persecution of these has become so great that
it seems doubtful if many young birds of any species now survive. At the
same time a very large trade seems to have developed in recent years in the
marketing of wild birds as ‘pets’. This is based on the capture of young
colonial seabirds, and the trapping and netting of any other available birds,
of which waders are probably at greatest risk. Flightless flocks of waders and
terns are a common sight in the house compounds of most villages in the
Maldives. It would seem that considerable colonies of breeding seabirds
such as terns, boobies, shearwaters, frigatebirds and tropicbirds could be
built up very quickly if the persecution of both adults and young ceased, and
breeding colonies were given close protection. Similarly, the conservation
of turtles could provide a further important attraction.
Much of the trade in birds passes through the resort islands, possibly
because of the frequent contacts they maintain with the capital Male. The
possibility that birds are being exported from the Maldives was not established
on the 1993 visit, but birds are certainly imported, particularly from Sri
Lanka. Apparently the crews of many merchant vessels visiting Maldivian
waters carry birds with them, and the significance of this custom may not be
appreciated in the assessment of records of unusual vagrants in this region.
The photographs by Ahamed Shafeeg were of birds provided by islanders,
mostly fishermen, and were captured within the Maldives, where fishermen
1994
Birds of the Maidive Islands
5
remain within territorial waters. Bird-catching parties also travel to
uninhabited islands for the express purpose of netting birds. Some information
was obtained on the market values of birds and these are included in Table
1. The exchange rate in 1994 was 17 Maldivian rupees (Rs) to £1 sterling
(approximately Rs 1 1 = US$1.00).
Table 1. Market value of certain birds
6
J. S. ASH and ALI SHAFEEG
Forktail 10
Following the name of each species, the local Maldivian name, where
known, is included in parentheses. However, names sometimes vary
between atolls, and spelling is often highly variable. Subspecies are given
where they are established from collected specimens. Next, also given in
parentheses are the observations by J. S . A. for visits from 2 1 April to 1 4 May
1 984 to the northern atolls (Ash 1 984b), and from 4- 1 8 November 1 993 to
the southern atolls; the latter with Richard Howard and Alick Moore with
the Bat Conservation Trust Expedition (Ash et al. in prep.), as are also the
notes on the photographs by Mr Ahamed Shafeeg. Then follows a brief
summary of the species’ status in the Maldives, together with a list of the
islands and/or atolls from which they are recorded - the latter are italicized
if the species is known to have bred there (months of the year are given in
lower-case Roman numerals); and lastly a list of the relevant references to
the published and unpublished literature. Many of the earlier records are
imprecise as to dates, and often localities. In order to avoid much repetition
the references under each species are mentioned by numbers only. Much
difficulty was experienced with atoll names in the Maldives, and it is hoped
that the map and the list of names in Appendices 1 and 2 will help to identify
the various old and new names, bearing in mind the absence of an agreed
consensus of opinion on the spelling of names.
The first list of the birds of the Maldives by Gadow and Gardiner (1903)
included 24 species; Phillips’ visit in 1956-1957 increased this total to 63
(Phillips and Sims 1 958b) and, following a further visit and more observations,
the total reached 1 12 (Phillips 1963). Additions since then result in a total
of 147 species. The outstanding collection of photographs formed by Mr
Ahamed Shafeeg of the Council for Research on Maldivian History and
Culture deserves special mention. There are 1 2 species represented in these
photographs for which there are no other Maldivian records. Part of this
collection remains unexamined, so that more additions can be expected.
ANNOTATED LIST
Domestic Fowl Gallus gallus (male: Haa; female: Kukulhu). (Feral
populations appeared to be established on K. Vilingili in 1984, and there
were several birds and a pair with a brood on uninhabited M. Boahuraa on
7 November 1993. They are said to occur in a feral and domesticated state
throughout the Maldives. Refs 6, 13.
Cotton Pygmy-Goose Nettapus coromandelianus (no local name). N. c.
coromandelianus. One in xii and several in x on S. Gamu. Said also to be
imported from Sri Lanka and India. Refs 25, 33.
Northern ShovelerH/2<25 clypeata (Reyru; no specific name). (In 1993: L.
Maandhoo, one on 11 November and L. Maabaidhoo, one caged on 14
1994
Birds of the Maidive Islands
7
November.) Reported to be a regular winter visitor with up to seven
together, xi-i. Also recorded Seenu Atoll. Refs 6, 25, 32, 33.
Northern Pintail Anas acuta (Ilifathi reyru). (A bird captured in 1982 on
Baa Atoll was photographed [Shafeeg] .) Rare visitor recorded three or more
times in x, xii, i. Also recorded Seenu Atoll. Refs 25, 32, 33.
Garganey Anas querquedula (Kuburu reyru). (A bird captured in 1982 on
Baa Atoll was photographed [Shafeeg], In 1993: M. Muli, a caged bird on
7 November had been brought from K. Male eight years previously. L.
Maandhoo, one on 10 November and four on 1 1 November.) Reported as
being a regular winter visitor in flocks of up to 25 birds, ix-i. Also reported
B. Hithaadhoo; Seenu Atoll. Refs 6, 25, 27, 32, 33.
Common Teal A nas crecca (no local name). A. c. crecca. An occasional
winter visitor in flocks of up to 10 birds. Recorded K. Male; Baa Atoll;
Shaviyani Atoll; Seenu Atoll in x, and others unspecified. Other dates are
unavailable. Refs 2, 14, 25, 27, 33.
Ferruginous Pochard Aythya nyroca (Rathu reyru). (1993: two on 10
November on L. Maandhoo. Vagrant, with only one previous record in xi
on S. Gamu, although Ahamed Shafeeg refers to it as a common migrant xi-
i. Refs 6, 25, 32, 33.
Tufted Duck Aythya fuligula (Ran rathu reyru). (A captured bird, for
which there are no details of date or locality, was photographed [Shafeeg] .)
Reported to be a fairly frequent winter visitor xi-i. Also recorded: K. Male.
Refs 2, 25, 27, 32.
Eurasian Hoopoe Upupa epops (Funaagandu dhooni). U. e. epops. (A bird
captured at K. Male in 1981 was photographed [Shafeeg].) A previous
record in autumn on S. Gamu and a captured bird on R. Kadholhudhoo in
October 1990 (R. C. Anderson). Refs 3, 4, 32, 33.
Indian Roller Coracias benghalensis (no local name). Rare winter visitor
with two records in xi on Seenu Atoll. Ref 33.
[Common Kingfisher Alcedo atthis (no local name). An unidentified
kingfisher, possibly this species, was seen at K. Lhosfushi in i. Ref 21, 22.]
Blue-tailed Bee-eater Merops philippinus (no local name). (1993: two on
16 November on A. Hurasdhoo clearly identified as this species and not
Blue-cheeked Bee-eater M. persicus. The first record for the Maldives. Ref
6.
European Bee-eater Merops apiaster (no local name). Recorded once
overwintering on S. Gamu, i-iii. This is apparently a unique winter record
outside Africa. Refs 2, 25, 33.
Indian Cuckoo Cuculus micropterus (Fuggahu guraa). A record of one on
K. Vilingili in ii is the only published record. Ahamed Shafeeg states that it
occurs in most years either singly or in groups of two or three, arriving in
easterly winds. Ref 13.
8
J. S. ASH and ALI SHAFEEG
Forktail 10
Common Cuckoo Cuculus canorus (Fuggahu guraa) . A regular winter visitor
recorded from S. Gamu in ix-i. Ahamed Shafeeg states that formerly it came
with easterly winds, but that there have been very few in recent years. Refs
2, 25, 32, 33.
[Banded Bay Cuckoo Cacomantis sonneratii (Fuggahu guraa) . A bird fitting
the description of this species was seen and photographed one autumn in the
late 1960s on S. Gamu, but little detail is available and the record is best
treated as unconfirmed. Ref 33.]
Grey-bellied Cuckoo Cacomantis passerinus (Fuggahu guraa) . Rare winter
visitor with two records in xi and i, on S. Gamu. Refs 2, 25, 33.
Asian Koel Eudynamys scolopacea (male Kaalhukoeli; female Dindin koeli).
E. s. scolopacea. (Common and widespread in April and May 1984, and in
November 1993, even on islands where there are no House Crows, so that
they must wander a great deal. Noted on: K. Male, K. Vilingili, K.
Biyaadhoo and K. Guraadhoo; H. A. Maafahi, H. A. Maarandhoo and H.
A. Vashafam, where there was still a juvenile with basal feather sheaths on
6 May 1984 [Ash]; M. Mulah; L. Maamendhoo, L. Maandhoo, L.
Hithadhoo, L. Mendhoo, L. South Athahedha, L. Fares, L. Vadinolhu, L.
North Athahedha, L. Isdhoo (where also a juvenile and two pulli on 14
November 1993), L. Maabaidhoo; Dh. Dhoores; A. Feridhoo.) Also
recorded: Baa/Haa, Noonu/Shaviyani and Lhaviyani Atolls; K. Hulhule, K.
Male (but no longer breeds); S. Gamu in x-i. Ahamed Shafeeg states that
they are resident and widespread in moderate numbers throughout the
archipelago, parasitising the House Crow. Refs 2, 4, 5, 6, 12, 13, 14, 21,
22, 25, 27, 33.
[Rose-ringed Parakeet Psittacula krameri (Bodu guraa). (A captured male
on Kaafu Atoll in 1 98 1 had been imported and was photographed [Shafeeg] .)
Ahamed Shafeeg states that the above and the following are imported by
man and later escape or are released; recently some resort islands have been
introducing free-flying birds. Refs 4, 6, 32.]
[Parakeet Psittacula and/or Hanging-Parrot Loriculus. (Two seen briefly
at K. Male on 21 April 1984 [Ash], and another on L. Maandhoo on 12
November 1993.) There are many reports over the years from various
islands of unidentified parakeets, which suggest that there is a small resident
population or that immigrants occur. Only one of those seen has been
identified satisfactorily, and the circumstances of its occurrence verified
(see P. krameri above). Refs 2, 4, 6, 14, 25, 27, 32.]
Himalayan Swiftlet Collocalia brevirostris (Forikey). An occasional winter
visitor with four records in xi-i on K. Male and S. Gamu. Refs 25, 27, 33.
White-throated Needlet ail Hirundapus caudacutus (Forikey). One record
in x on Seenu Atoll. Ref 33.
Common Swift Apus apus (Forikey). A regular visitor, ix-xi and iv-v, to S.
Gamu. Refs 2, 25, 33.
1994
Birds of the Maidive Islands
9
Pallid Swift Apus palhdus (Forikey). Rare winter visitor with two records
in ix and x on Seenu Atoll. Ref 33.
Little Swift Apus affinis (Kuda forikey). An irregular winter visitor with
about six records on S. Gamu. Refs 2, 25, 33.
Short-eared Owl /Bio flammeus (Bakamoonu). Irregular northern winter
visitor, sometimes in considerable numbers, x-iv. Owls are considered bad
omens and are killed on sight. Recorded from B. Goidhoo Fehen Fuladhoo,
N. Kedhikolhu, K. Male, and Seenu and Gaafu Alifu/Gaafu Dhaalu Atolls.
Refs 2, 14, 25, 27, 33.
Rock Pigeon Columba livia. (Feral populations were recorded in November
1 993: six on M. Mulah; two on L. Maamendhoo, 1 2 on L. Maandhoo, three
on L. Kalhaidhoo; one on A. Feridhoo. Ref 6.)
European T urtle-Dove Streptopelia turtur (Valukotharu). (A bird captured
on Vaavu Atoll in 1981 was photographed [Shafeeg].) Not otherwise
recorded south-east of Pakistan. Refs 2, 32.
Oriental Turtle-Dove Streptopelia orientalis (Valukotharu). An irregular
winter visitor, recorded on Seenu Atoll in ix and x. Ref 33.
Spotted Dove Streptopelia chinensis (no local name). (One heard, but not
seen, in thick cover on A. Hurasdhoo on 16 November 1993). No previous
record for the Maldives. Ref 6.]
[Emerald Dove Chalcophaps indica (Valukotharu). A bird, possibly of this
species, was recorded on K. Vilingili in ii. Ref 13.]
White-breasted Waterhen Amauromis phoenicurus (Kan’bili). A. p.
phoenicurus, A. p. maldivus. (Common and widespread in April-May 1984
on K. Kurumba, K. Vilingili and K. Guraadhoo; H. A. Dhidhdhoo and H.
A. Maarandhoo [Ash], 1993: one on 6 November on M. Muli; 10 and five
on 10 and 11 November, of which one was alive in a snare, on L.
Maandhoo.) Widespread resident in all the atolls. Breeds v-x. Also
recorded: Kaafu Atoll: K. Hulhule, K. Gaagadu, K. Himmafushi, K.
Gaafaru; Alifu Atoll; Lhaviyani Atoll; Seenu Atoll. Refs 2, 4, 5, 6, 12, 13,
14, 25, 26, 27, 33.
Watercock Gallicrex cinerea (Kulhee kukulhu). Apparently an uncommon
resident or breeding visitor (vi-vii) . Recorded Kaafu Atoll and Seenu Atoll,
and on Sh. Maakadoodhoo by Ahamed Shafeeg. Refs 2, 25, 27, 32, 33.
Common Moorhen Gallinula chloropus (Olhuvalu kabili). (A nest with two
eggs and the pair of adults, on Gn. Fua Mulaku in August 1983, were
photographed [Shafeeg] ) . Ahamed Shafeeg stated that this species was first
found there in 1945, and that it had never been seen elsewhere in the
Maldives. Ref 6, 32.
Common Coot Fulica atra (no local name). One captured on Baa Atoll in
1981 was photographed [Shafeeg]. This is the only record from the
Maldives. Ref 32.
10
J. S. ASH and ALI SHAFEEG
Forktail 10
Pintail Snipe Gallinago stenura (Dhushin ilolhi). Apparently a regular
winter visitor, xi-i, in moderate numbers in parties of up to six. Recorded:
K. Hulhule; Seenu Atoll. Refs 2, 25, 27, 33.
Swinhoe’s Snipe Gallinago megala (Dhushin ilolhi). A winter visitor
recorded once only on S. Meedhoo in xii. Refs 25, 33.
Common Snipe Gallinago gallinago (Dhushin ilolhi). G. g. gallinago.
Apparently a regular winter visitor recorded in x-i, from Seenu Atoll only.
Refs 2, 12, 14, 25, 33.
Black-tailed Godwit Limosa limosa (Eshunga ilolhi). (One captured in K.
Male in 1980 was photographed [Shafeeg].) This would appear to be the
only record for the Maldives; although Ali and Ripley (1984) refer to it as
a vagrant there, the original record cannot be traced. Refs 2, 4, 32.
Bar-tailed Godwit Limosa lapponica (Bulhi thun’bi ilolhi). L. 1. lapponica.
(A bird captured on K. Male in 1983 was photographed [Shafeeg]. In 1993:
L. Hithadhoo, one caged on 12 November; L. Kunahandhoo, two on 12
November; L. Fares, one on 13 November; L. Kalhaidhoo, one on 15
November.) Apparently an annual visitor in small numbers, vi-i. Refs 2, 4,
6, 25, 27, 32, 33.
Whimbrel Numenius phaeopus (Bulhi thubi). N. p. phaeopus. (Captured
birds on K. Male in 1981 and 1983 were photographed [Shafeeg] . In 1 984:
singly on K. Hulhule on 21 April and on K. Vilingili on 13 May 1984; one
on H. A. Dhidhdhoo, 3 May 1984 [Ash], In 1993, M. Muli, one caged on
7 November; M. Mulah, one caged on 8 November. L. Maandhoo, two on
1 0 November, six on 1 1 November, and five on 1 2 November; L. Hithadhoo,
two caged on 12 November; L. Kunahandhoo, 10 and four caged on 12
November; L. South Athahedha, three on 12 November; L. North
Athahedha, two on 13 November; L. Fares, two on 13 November; L.
Maabaidhoo, two caged on 14 November, and one on 15 November.)
Regular winter visitor, viii-iii, and many oversummer. Also recorded:
Seenu, Raa/Baa and Noonu/Shaviyani Atolls. Refs 2, 4, 6, 12, 13, 14, 22,
25, 27, 32, 33.
Eurasian Curlew Numenius arquata (Bodu bulhi thubi). N. a. orientalis. (A
bird captured on 25 March 1982 on Lh. Naifaru was photographed
[Shafeeg], In 1993 on L. Hithadhoo, four caged on 12 November; L.
Kunahandhoo, two on 12 November; L. Fares, one on 13 November; L.
Maabaidhoo, one on 15 November; Dh. Dhoores, one on 16 November.)
A regular winter visitor in small numbers; some oversummer. Also recorded
on K. Lankanfushi; S. Gamu and S. Hithaadhoo. Refs 2, 4, 6, 8, 1 2, 20, 25,
27, 32, 33.
Common Redshank Tringa totanus (Rathafai ilolhi). T. t. totanus. A regular
winter visitor in small numbers, ix-iii. Recorded on K. Male and Seenu
Atoll. Refs 2, 25, 27, 33.
1994
Birds of the Maidive Islands
11
Marsh Sandpiper Tringa stagnatilis (Furedhdhe ilolhi). An irregular winter
visitor, ix and x recorded from Seenu Atoll. Ref 33.
Common Greenshank Tringa nebularia (Chon chon ilolhi). (One, H. A.
Maafahi on 1 May 1984 [Ash], In 1993 on M. Muli, one caged on 7
November; L. Hithadhoo, one caged on 12 November; L. Kunahandhoo,
one seen, and two caged, on 1 2 November.) A northern visitor in moderate
numbers, up to nine together; some oversummer. Also recorded: K. Male
and G. A. Vilingili (one captured individual seen on 7 February 1994 by R.
C. Anderson); Noonu/Shaviyani Atolls. Refs 2, 3, 4, 6, 12, 22, 25, 27, 33.
Wood Sandpiper Tnnga glareola (Fidhan ilolhi). Annual winter visitor viii-
ii, in small numbers up to six together. Recorded: K. Male; S. Gamu. Refs
2, 25, 27, 33.
Terek Sandpiper Tringa cinerea (no local name). (In 1993, L. Fares, three
on 1 3 November; L. Hithadhoo, two caged on 1 2 November.) An irregular
winter visitor with several records on S. Gamu in xi and xii. Refs 6, 25, 33.
Common Sandpiper Tringa hypoleucos (Findhana). (Two, K.
Kan’doomaafushi on 27 April and single birds on H. A. Maafahi and H. A.
Maarandhoo on 1 and 5 May 1984, respectively [Ash], 1993 summary: 36
birds on nine days, 4-16 November, on K. Male; M. Muli; L. Maandhoo,
L. Kunahandhoo, L. South and North Athahedha, L. Fares, L. Vadinolhu,
L. Bodufinolhu, L. Isdhoo and one caged on L. Kunahandhoo; Dh.
Dhoores.) Regular winter visitor in moderate numbers viii-v to all atolls.
Also recorded: K. Hulhule, K. Male and K. Vilingili; Seenu Atoll. Refs 2,
4, 6, 12, 13, 14, 25, 27, 33.
Ruddy Turnstone Arenaria interpres (Rathafai). A. i. interpres. (Seven
captured birds on K. Male were photographed together in 1983 [Shafeeg];
three and one on H. A. Dhidhdhoo on 1 and 6 May respectively, and one
on H. A. Maarandhoo on 4-5 May 1 984 [Ash] . In 1 993, M. Boahuraa, one
on 6 November. L. Maandhoo, two on 1 0 November; L. Fonadhoo, one on
10 November; L. Maandhoo, two on 1 1 November; L. South Athahedha,
six on 1 3 November; L. North Athahedha, three on 1 3 November; L. Fares,
four on 1 3 November. Also a total of 26 caged: one M. Muli, one M. Mulah,
1 0 L. Hithadhoo, 2 1 L. Kunahandhoo, and one L. Fares, two A. Feridhoo.)
Winter visitor in flocks of up to 200; some oversummer. Also recorded: K.
Male; Alifu Atoll; Lhaviyani Atoll; S. Gamu. Refs 2, 4, 6, 8, 12, 14, 22, 25,
27, 32, 33.
Sanderling Calidris alba (Kirru bondun) . Rather uncommon winter visitor
to S. Gamu only, x-iii. Refs 2, 12, 25, 33.
Little Stint Calidris minuta (Kirru bondun). (1993: L. Maabaidhoo, one
caged on 14 November.) A regular winter visitor in small numbers xi-i.
Recorded K. Male and S. Gamu. Refs 2, 6, 25, 27, 33.
12
J. S. ASH and ALI SHAFEEG
Forktail 10
Temminck’s Stint Calidris temminckii (Kirru bondun) . A few apparently on
passage on S. Gamu, v and x-xi. Refs 2, 25, 27, 33.
Long-toed Stint Calidris subminuta (Kirru bondun). Apparently a winter
visitor in small numbers to S. Gamu, x-ii. Refs 2, 25, 33.
Dunlin Calidris alpina (Kirru bondun). C. a. alpina. (1993: L. Fares, one
on 1 3 November.) Probably a winter visitor in small numbers to S. Gamu,
xi-ii. Refs 2, 6, 12, 25, 33.
Curlew Sandpiper Calidris ferruginea (Bondana ilolhi). (In 1993 on L.
Maamendhoo, one caged on 10 November; L. Kunahandhoo, two on 12
November.) Winter visitor in large numbers, in flocks of up to 500 birds,
and some oversummer, v-iii. Recorded also: S. Gamu. Refs 2, 6, 12, 25,
27, 33.
Spoonbill Sandpiper Eurynorhynchus pygmeus (Samsaa dhooni). Ahamed
Shafeeg states that it was observed three times on S. Gamu in 1 964, and on
Haa Alifu and Haa Dhaalu Atolls in the same year. No photographs or
further details are available, so the records are unacceptable, unfortunately.
Ref. 32.]
Ruff Philomachus pugnax (no local name). Rare winter visitor, with three
records x-xi on S. Gamu. Refs 2, 25, 33.
Eurasian Oystercatcher Haematopus ostralegus (no local name). (1993:
Laamu Atoll: one caged on 1 2 November had been caught locally.) The first
record for the Maldives. Ref 6.
Black-winged Stilt Himantopus himantopus (Theyravaa ilolhi). (A bird
captured on K. Male in 1982 was photographed [Shafeeg].) Uncommon
visitor with five records, of which one in xi. Also recorded: S. Gamu. Refs
2, 25, 32, 33.
Pacific Golden-Plover Pluvialis fidva (Bilehmaa dhushin) . (A bird trapped
on Raa Atoll in 1 98 1 was photographed [Shafeeg] . In 1 993, L. Kunahandhoo,
one on 12 November; L. Hithadhoo, one caged on 12 November.) A
common winter visitor in flocks of up to 50 birds. Also recorded: K. Male;
S. Gamu; N. Bodulhaimendhoo. Refs 2, 4, 6, 12, 14, 25, 27, 32, 33.
Grey Plover Pluvialis squatarola (Alaka). (One, H. A. Dhidhdhoo on 1 May
1984 [Ash] .In 1 993, on M. Muli, one caged on 7 November. L. Hithadhoo,
three caged, and a further two caged on L. Kunahandhoo, on 1 2 November;
singly on L. Fares, L. South Athahedha and L. Bodufinolhu on 13
November; L. Maabaidhoo, two, and one caged, on 14 November; Dh.
Dhoores, one on 15 November.) A common winter visitor, and some
oversummer. Also recorded from K. Male; S. Gamu; H. A. Dhidhdhoo.
Refs 2, 6, 12, 21, 25, 27, 33.
Common Ringed Plover Charadrius hiaticula (An’goti bon’dana). C. h.
tundrae. An annual winter visitor in small numbers, x-iii. Recorded: K. Male
and S. Gamu. Refs 2, 25, 27, 33.
1994
Birds of the Maidive Islands
13
Little Ringed Plover Charadrius dubius (Findon) . C. d. jerdoni. Probably
an annual winter visitor in small numbers, although only known from S.
Gamu, xi-ii. Refs 25, 33.
Kentish Plover Charadnus alexandrinus (Kiru bon’dana). Occasional in
winter, x-ii on S. Gamu. Refs 2, 25, 33.
Mongolian Plover Charadrius mongolus (Findon). C. m. atrifrons. (One on
H. A. Dhidhdhoo on 6 May 1984 [Ash], In 1993, L. Kunahandhoo, one
caged on 12 November.) Common regular winter visitor, viii-v. Also
recorded: K. Male; S. Gamu; Lhaviyani Atoll. Refs 2, 4, 6, 25, 27, 33.
Greater Sand Plover Charadrius leschenaultii (‘ Valu bon’dana) . (In 1 993,
L. Hithadhoo, one caged and L. Kunahandhoo, one caged, on 1 2 November;
L. Fares, seven on 13 November; L. Bodufmolhu, one on 13 November.)
Regular winter visitor in small numbers, viii-iv; also v and vi. Also recorded
from K. Dhoonidhoo; S. Gamu. Refs 2, 6, 25, 27, 33.
Caspian Plover Charadrius asiaticus (no local name). Only recorded once:
5. Gamu. Refs 2, 25, 33.
Sociable Lapwing Vanellus gregarius (no local name). One certain record
only, on Seenu Atoll, ix. Refs 25, 27, 33.
Crab Plover Dromas ardeola (Eshungu on Seenu, Theyravai on Male,
Moola lumba a juvenile on Male) . (A bird captured on K. Male in 1 98 1 was
photographed [Shafeeg], In 1984: two on H. A. Dhidhdhoo on 2 May and
two on H. A. Bibera on 6 May [Ash], In 1993 on M. Muli, two on 7
November, two caged on 8 November. L. Kunahandhoo, nine and one
caged on 12 November; L. Hithadhoo, one caged on 12 November; L.
Ziyaaraifushi, six on 13 November.) Common and widespread and possibly
resident, recorded xii-i and v-vi, viii. Also recorded: Sh. Funadhoo; Gaafu
Alifu/Gaafu Dhaalu Atolls; Alifu Atoll; and on Th. Omadhoo. Refs 2, 3, 4,
6, 14, 22, 25, 27, 32, 33.
Oriental Pratincole Glareola maldivarum (Almalu guraa). Common
visitor x-iii in flocks of up to 25, and occasionally breeds in xii, on S'. Gamu.
Refs 2, 25, 33.
Antarctic/Brown/South Polar Skua Catharacta antarctica/lonnbergi/
maccormicki (Kukulhumaadhooni). At least 11 birds reported. (Five birds
captured on K. Male consisted of two adult lonnbergi and an unidentifiable
bird in 1 983 which were photographed [Shafeeg] . Two maccormicki without
details were also photographed [Shafeeg] . A pinioned bird on 27 April 1 984
on K. Kan’doomaafushi was stated to have been captured five years earlier,
and was identified at the time as antarctica [Ash].) Three unidentified to
species, of which one was on S. Gamu in 1961, and two single birds were
seen by J. Belien in 1983 and 1984 (localities unknown). Two specifically
unidentified pinioned birds were on K. Male in January 1994 (R. C.
Anderson). Refs 2, 3, 4, 25, 31, 32, 33.
14
J. S. ASH and ALI SHAFEEG
Forktail 10
White-eyed Gull Lams leucophthalmus (Boyahguirey dhooni). One collected
in June 1879 was the first record for the Maldives and the Oriental Region.
(A second example, an adult captured in 1983 at an unknown locality, was
photographed [Shafeeg] .) Ahamed Shafeeg states that one or two birds are
captured almost every year by fishermen, and sometimes sailors of merchant
vessels bring them in. Refs 29, 32.
Sooty Gull Lams hemprichii (Boyahguirey dhooni) . (An immature captured
at an unknown locality and on an unknown date was photographed
[Shafeeg] .) Ahamed Shafeeg states that in some years one or two birds come
to the Maldives, and also that sometimes sailors bring them in. Refs 4, 32.
Yellow- legged Gull Lams cachinnans (Boyahguirey dhooni). (Two
adults captured on K. Male in 1981 and 1982 had pale grey mantles and
yellow legs, and there was a third without date from Laamu Atoll; all were
photographed [Shafeeg] and are assumed to relate to this species. An
immature on S. Gamu on 29 September 1970 was either this species or
fuscus (ref 33), and a similar bird but without details was photographed
[Shafeeg].) Refs 4, 32, 33.
Lesser Black-backed Gull Lams fuscus (no local name). (An adult
captured on Laamu Atoll in 1 98 1 was photographed [Shafeeg] .) This is the
only record from the Maldives. Refs 4, 31, 32.
Herring/Lesser Black-backed Gull Lams argentatus /fuscus. (An adult
which was either L.f fuscus or L. a. heuglini without details, was photographed
[Shafeeg].) Refs 4, 32.
Great Black-headed Gull Lams ichthyaetus (Boakalhu gohorukey). (A
near-adult captured in 1 983 on Laamu Atoll was photographed [Shafeeg] .)
This is the only record from the Maldives. Refs 4, 31, 32.
Brown-headed Gull Lams bmnnicephalus (Boyahguirey dhooni). (One
captured on K. Male in 1981 and another on Gn. Fua Mulaku in 1 983 were
photographed [Shafeeg].) These are the only records from the Maldives.
Refs 4, 31, 32.
Common Black-headed Gull Lams ridibundus (Boyahguirey dhooni).
(The following birds captured on K. Male were photographed [Shafeeg] : a)
adult in 1981; b) one in 1982 - identification uncertain but probably this
species rather than L. bmnnicephalus ; c) one immature in 1983; d) an
undated adult from an unrecorded locality.) There is only one previous
record of this occasional visitor, from S. Gamu. Refs 2, 4, 25, 32, 33.
Gull-billed Tern Sterna nilotica (Kanifulhu dhooni). S. n. nilotica. Only
seen singly, or in small numbers, occasionally, i, iii, iv, ix, xii, but reported
to breed iii-iv. Also recorded: K. Male; Seenu Atoll. Refs 2, 25, 27, 31,33.
Caspian Tern Sterna caspia (Miyaremu dhooni). Uncommon visitor, iv, ix-
xi and i, up to four together, recorded K. Kassanfaru and Seenu Atoll. Refs
2, 25, 27, 31, 33.
1994
Birds of the Maidive Islands
15
Lesser Crested Tern Sterna bengalensis (Ainmathee gaa dhooni). S’, b.
bengalensis. (In 1993, K. Eboodhoo, one on 4 November; M. Mulah, 1-5
on 9 November; L. Ziyaaraifushi, 25 on 13 November and atoll reef, 10 on
14 November; Dhaalu Atoll one on 15 November, Dhoores, one on 16
November, and off Dhoores, two on 16 November.) Apparently resident
in moderate numbers, but only reported x-v. Also recorded: K. Thulhaagiri
and K. Vihamanafushi ( Kaafu Atoll); Seenu and Alifu Atolls. Refs 2, 4, 6,
25, 27, 31, 33.
Great Crested Tern Sterna bergii (Bodu gaa dhooni). S’, b. velox. (One on
H. A. Dhidhdhoo on 2 May 1984 [Ash], In 1993: K. Male, one on 4
November; K. Giraavaru, two on 17 November, K. Eboodhoo, 1 1 on 4
November; K. Dhigufinolhu, one on 4 November. Off Kaafu Atoll: 15 on
4 November. K. Muli, 1 0 on 7 November; M. Mulah, 50+ on 9 November,
and off M. Mulah, 13 on 9 November; L. Fares, two on 13 November and
L. Ziyaaraifushi, two plus on 13 November; Dhaalu Atoll: three on 15
November; A. Hurasdhoo, one on 1 6 November.) Apparently resident and
widespread in small numbers; Maldivians state that they breed on K.
Foojaadi in iv. Also recorded: K. Hulhule, K. Vihamanaafushi and K.
Dhoonidhoo; Seenu, Alifu, and Lhaviyani Atolls. Refs 2, 4, 6, 22, 25, 27,
31, 33.
Roseate Tern Sterna dougallii (Valla). S. d. korustes. (In 1993 seven caged
birds, six on L. Hithadhoo and one on L. Kunahandhoo on 12 November.)
Frequently seen and reported to breed K. Foojaadi , iii-v. Ahamed Shafeeg
stated in 1993 that it bred throughout the Maldives. Refs 2, 25, 27, 31.
Black-naped Tern Sterna sumatrana (Kiru dhooni). S. 5. mathewsi. (1984:
widespread in small numbers, maximum 14 together in April-May. Noted
on K. Furannafushi (where stated to breed on an adjoining islet), K. Gulhi,
K. Lankanfinolhu, K. Kagi, K. Bandos; Lh. Hinnavaru; H. A. Dhidhdhoo,
H. A. Filladhoo, H. A. Vashafaru; N. Huivani, N. Vattaru [Ash], In 1993:
one on 5 November on K. Biyaadhoo. Vattaru Channel: five on 5 November.
Meemu Atoll: 40+ (breeding?) on 9 November. L. Ziyaaraifushi , 20+ on 13
November, where breeding colony with only one clutch of one egg and two
half-grown young were surviving. Off Alifu Atoll: six on 16 November. K.
Grawa and off K. Male, single birds on 1 7 November.) The most abundant
and widespread tern, present throughout the year, sometimes in large
flocks; breeds iii-v. Also recorded: K. Foojaadi ; S. Gamu, S'. Bushy Islet and
S. Tern Islet, Alifu, Lhaviyani and Noonu/Shaviyani Atolls. Refs 2, 4, 6, 8,
14, 20, 22, 23, 25, 27, 28, 31, 33.
Common Tern Sterna hirundo (Kirra dhooni). S. h. tibetana. (Fifteen adults
and one immature on H. A. Bibera on 6 May 1984 [Ash], In 1993, an
immature photographed on L. Maandhoo on 10 November. The
identification of a number of caged birds, possibly of this species, was not
established.) Previously the only other substantiated records were from
16
J. S. ASH and ALI SHAFEEG
Forktail 10
Seenu Atoll, where it is an irregular winter visitor x-ii. Dr. R. C. Anderson
has found many in January and February 1994 in the 1°° Channel, and
probably some of the other reports of flocks of terns at sea belong here. Refs
3, 6, 25, 32, 33.
Little Tern S7mza a/6z/rons (Bodu dhooni) . S', a. albifrons. One record only
from Seenu Atoll in xi. Refs 2, 25, 33.
Saunders’s Tern Sterna saundersi (Bon’dhu dhooni). (In 1993, all small
terns were regarded as this species rather than albifrons. K. Biyaadhoo, one
on 5 November; M. Muli, five on 6 November, 10+ on 7 November, and
25 on 8 November; L. Kunahandhoo, one caged on 12 November.)
Numerous resident throughout the Maldives, reported breeding in iii and
iv. Recorded from K. Foojaadv, Seenu Atoll. Refs 2, 6, 25, 27, 31, 33.
White-cheeked Tern Sterna repressa (no local name). (One captured on
Meemu Atoll in 1983, and another without details, were photographed
[Shafeeg], In 1993: a first-winter bird on 1 1 November on L. Maandhoo.)
Possibly an overlooked species owing to confusion in non-breeding plumages
with S. hirundo and S. dougallii. Refs 6, 32.
Bridled Tern Sterna anaethetus (Vaali). (In 1993, M. Muli, two probables
on 6 November; L. Kunahandhoo, one caged on 12 November.) Reported
to visit the Maldives in iii and iv to breed on K. Foojaadi , although there was
a captured juvenile on K. Vilingili in ii; recorded S. Gamu in ii and vi. Refs
2, 3, 6, 25, 27, 31, 33.
Sooty Tern Sterna fuscata (Valli; Baindu in the north). (In 1993, Vattaru
Channel, 200+ on 5 November; Meemu Atoll, four on 9 November;
Kudahuvadu Channel, 40 on 9 November; Veimandu Channel, 42 on 15
November; Dhaalu Atoll: one on 15 November, three on 16 November.)
Previously only recorded from Seenu Atoll, where reported to breed iii and
iv. Refs 2, 6, 14, 25, 27, 31, 33.
White-winged Tern Chlidonias leucopterus (Kiru dhooni). (In 1993, L.
Maandhoo, one on 1 2 November.) One near L. Maavah on 2 October 1 992
(R. C. Anderson). The above are the only records away from Seenu Atoll,
where it is a fairly regular winter visitor in small numbers, up to six together.
Refs 2, 3, 6, 25, 33.
Brown Noddy stolidus (Maaraga). A. s. pileatus. (A captured bird on
K. Male in 1980 was photographed [Shafeeg]; four off K. Male on 27 April,
and three at K. Gaafaru, 29 April 1 984 [Ash] . In 1 993, M. Muli, one caged
on 7 November; L. Maabaidhoo, two on 1 5 November; Veimandu Channel,
six on 1 5 November; Dhaalu Atoll: 40 on 15 November; off Alifu Atoll, 1 1
on 16 November; Alifu/Male Channel, 24 on 17 November.) Common in
large numbers throughout the year; Maldivians report breeding but only
one definite record known, vi-vii. Also recorded K. Thulhaagiri, K.
Medhufinolhu; Gaafu Alifu/Gaafu Dhaalu Atolls; Seenu Atoll: Gamu and
Bushy Islet. Refs 2, 4, 6, 8, 1 1, 12, 20, 22, 25, 27, 31, 32, 33.
1994
Birds of the Maidive Islands
17
Lesser Noddy Anous tenuirostris (Kurangi). (One captured on Gaafu Alifu/
Gaafu Dhaalu Atoll in 1980 was photographed [Shafeeg]; four at K.
Maahaa Reef on 8 May 1984 [Ash], In 1993: off M. Raiymandhoo, one on
5 November; L. Ziyaaraifushi, 11 on 13 November, L. Vadinolhu, one
caught at night on 1 3 November (wing length 233 mm); Dhaalu Atoll, two
on 1 5 November, Dh. Dhoores, one on 1 6 November; K. Grawa, three on
17 November.) The 1899 record of breeding A. minutus on B. Mabaru is
considered to belong here, contra Phillips (1963); and Harrison (1983)
stated that A. tenuirostris breeds on the Maldives. These appear to be the
only records from the Maldives, until Dr R. C. Anderson noted it in 1993
as widespread throughout the Maldives, although it is much less common
than the Brown Noddy. Refs 2, 3, 4, 6, 14, 16, 25, 31, 32.
Common White-Tern Gygis alba (Kadhu valu dhooni). G. a. monte.
Apparently arrived this century to breed on Seenu Atoll, where it breeds
commonly throughout the year. Recorded S. Gamu and S. Maradhoo, and
recently recorded Gnyaviyani Atoll in November 1993, where regarded as
being commonest xii-iii (R. C. Anderson). Refs 2, 3, 8, 12, 20, 25, 27, 31,
33.
Osprey Pandion haliaetus (no local name). Vagrant. Once in vii and once in
xii at S. Gamu, and by Dr R. C. Anderson on A. Dhagathi on 30 January
1993. Refs 2, 3, 25, 33.
Oriental Honey-Buzzard Pemis ptilorhyncus (Bodu baazu) . P. p. orientalis.
Regular winter visitor, commonest xi-i, though some oversummer. Also
recorded S. Gamu, and K. Male and K. Vilingili. Refs 3, 13, 25, 33.
Western Marsh-Harrier Circus aeruginosus (Ehada). Reported to be a
regular winter visitor, recorded x-ii on K. Hulhule and S. Gamu. Refs 2, 25,
27, 33.
Pallid Harrier Circus macrourus (Baazu) . Regular winter visitor in varying
numbers, x-ii. Recorded: S. Gamu; Lhaviyani Atoll; northern atolls. Refs
2, 14, 25, 27, 33.
Montagu’s Harrier Circus py gar gus (Baazu). Common winter visitor x-iii,
together with an unknown number of unidentified ‘ringtails’ on S. Gamu
and on northern atolls. Refs 2, 14, 25, 27, 33.
[Common Buzzard Buteo buteo (Baazu). A rare winter visitor with several
records (one in i) at S. Gamu, presumed to relate to this species; also Gaafu
Alifu/Gaafu Dhaalu Atoll. Refs 25, 32.]
Lesser Kestrel Falco naumanni (Dhon surumuthi). F. n. naumanni.
Probably an annual winter visitor in small numbers, x-ii on S. Gamu. Refs
2, 25, 33.
Common Kestrel Falco tinnunculus (no local name). F. t. tinnunculus. An
annual visitor in moderate numbers, x-v on K. Hulhule, K. Vilingili and K.
Gaafaru; Alifu Atoll; S. Gamu. Refs 2, 12, 14, 25, 27, 33.
18
J. S. ASH and ALI SHAFEEG
Forktail 10
Amur Falcon Falco amurensis (Surumuthi) . Winter visitor in small numbers
xi-iii, with four or more records from S. Gamu. Refs 2, 25, 33.
Eurasian Hobby Falco subbuteo (no local name). (In 1993, L. Isdhoo, one
on 14 November (A. M. Hutson).) Regular visitor, xi-v. Ref 6, 33.
Peregrine Falcon Falco peregrinus (Baazu). Infrequent winter visitor,
recorded five times ix-xii on S. Gamu. Two in xii were identified as
Eleonora’s Falcon F. eleonorae in Duncan (1973) but are listed as peregrinus
in Strickland and Jenner (1978). Refs 2, 12, 25, 33.
White-tailed Tropicbird Phaethon lepturus (Dhan’difuludhooni). P. 1.
lepturus. (Two over K. Kaashidhoo and two on sea nearby, 8 May 1984
[Ash]; 18 captured birds (16 adults, two juveniles) photographed together
on Baa Atoll on 20 November 1983 [Shafeeg] . In 1 993, L. Maandhoo, three
plus on 10 November, four plus on 1 1 November, including two birds
entering presumed nesting holes high in Barringtonia trees, and two on 12
November; L. North Athahedha, one on 1 3 November.) Formerly plentiful
resident apparently throughout the Maldives, now decreasing. Breeds xi-
i, and probably later (iii, vii). Also recorded: K. Male and K. Thaburudhoo;
B. Thulhaadhoo and B. Hibalhidhoo , Gaafu Alifu/Gaafu Dhaalu, Lhaviyani
and Seenu Atolls. Dr R. C. Anderson noted eggs and chicks on G. A.
Hithaadhoo on 20 August 1994. Refs 2, 3, 4, 6, 14, 25, 27, 31, 32, 33.
Masked Booby Sula dactylatra (Hudhu maadhoni). (A captured adult on
Gaafu Alifu/Gaafu Dhaalu Atoll in 1982 was photographed [Shafeeg].)
Rare visitor, 1 -2 recorded on four occasions, viii and xi: K. Kassanfaru Reef;
S. Gamu; one in K. Male market on 30 August 1993 (R. C. Anderson).
Locally reported breeding (young observed) on Gaafu Alifu Atoll
unconfirmed. Refs 2, 3, 25, 27, 31, 32, 33.
Red-footed Booby Sula sula (Kadu heda maadhoni). (One subadult
captured in 1983 at K. Male was photographed [Shafeeg].) Dr R. C.
Anderson photographed captured individuals at A. Ukulhas on 1 5 September
1992 and on Gnyaviyani Atoll on 6 November 1993. A local report of
breeding on Gaafu Alifu Atoll has not been confirmed. Refs 3, 4, 31, 32.
Brown Booby Sula leucogaster (Kalhu maadhooni). 5. /. plotus. (Two
captured at K. Male, one in 1981 and the other in 1983, photographed by
Shafeeg, proved to be an adult and a juvenile.) A fairly common visitor,
most frequently xii-ii. Also recorded: Lhaviyani Atoll; K. Kassanfaru Reef;
and a captured bird at B. Thulhaadhoo on 19 August 1992 (R. C.
Anderson). Refs 2, 3, 4, 25, 27, 31, 32, 33.
Little Egret Egretta garzetta (Kuda lagana). (In 1993, L. Maandhoo, one
on 12 November; L. Kunahandhoo, one on 12 November; L. Isdhoo, one
on 1 4 November; L. Maabaidhoo, one caged on 1 4 November. A. Feridhoo,
one caged on 17 November.) Uncommon winter visitor recorded about
eight times; also on B. Eydafushi; S. Hulhudhoo. Refs 2, 6, 14, 25, 27, 33.
1994
Birds of the Maidive Islands
19
[Western Reef-Egret Egretta gularis (Bodu raabodhi). Ahamed Shafeeg
states one arrived with Cattle Egrets in 1990 and was photographed on B.
Thulhaadhoo, others had been reported elsewhere earlier. The photograph
has not been examined and no description is available. Ref 32.]
Gre\ Heron Ardea cinerea (Alhi maakanaa). A. c. rectirostris. (One to four
noted in April-May 1984 on K. Bandos, K. Hulhule, K. Gaafaru, K. Male,
K. Gulhi, K. Maafushi, K. Guraadhoo and K. Kan’doomaafushi; Lh.
Hinnavaru; N. Huivani; H. A. Dhidhdhoo, H. A. Thakandhoo and H. A.
Utheemu; H. Dh. Kumundhoo [Ash], In 1993, 1-11 noted (total of 72): on
K. Dhigufinolhu, K. Biyaadhoo; M. Muli, M. Mulah; Th. Fahala; L.
Maandhoo (10), L. Kunahandhoo, L. North and South Athahedha, L.
Fares, L. Ziyaaraifushi, L. Thundudhoshu, L. Isdhoo (1 1), L. Maabaidhoo,
L. Hurasdhoo (with two nests - one with two half-grown pulli in a lone tall
Ficus), and A. Feridhoo (only one captured bird seen).) Plentiful and
resident throughout. Occupied nests found vi-ii. Also recorded: R.
Bodufaru; K. Male, K. Vilingili and K. Gaafaru; S. Gamu and S. Hithaadhoo,
and Alifu Atoll. Refs 2, 4, 6, 8, 12, 13, 14, 20, 21, 22, 25, 27, 33.
Purple HERONHrdea purpurea (Dhabu maakanaa). (In 1993, a caged bird
on L. Hithadhoo on 12 November.) Probably a frequent visitor, at least
eight records of 1 -7 birds in vii and x-i, all except one from Seenu Atoll. Refs
6, 12, 25, 33.
Great Egret Casmerodius albus (Laganaa). C. a. modestus. (1984: one, H.
A. Dhidhdhoo, 1 May 1984 [Ash], 1993: a caged bird on L. Hithadhoo on
12 November.) Only three records of winter visitors, but Maldivians state
that it is frequent and Ali and Ripley (1987) list it as occurring in the
Maldives. Also recorded S. Gamu. Refs 2, 4, 6, 25, 33.
Intermediate Egret Mesophoyx intermedia (no local name). (A captured
bird on K. Male in 1982 was photographed [Shafeeg], In 1993 a caged bird
was photographed on L. Kunahandhoo on 12 November. The first records
for the Maldives.) Ref 2, 6, 32.
Cattle Egret Bubulcus ibis (Iruvaa hudhu). (A captive bird on 21 April
1984 in K. Male, where there were 1 1 birds in May [Ash], In 1993, two on
M. Mulah on 8 November; L. Kadhdhoo, one on 10 November, L.
Maandhoo, one on 1 0 November, L. Hithadhoo, one, and L. Kunahandhoo
one caged, on 12 November; Dh. Ribudhoo, one caged on 16 November.)
A regular visitor, arriving in small flocks in x-xi until iii-v; possibly bred
Seenu Atoll in ix. Also recorded: K. Dhiffushi and Seenu Atoll. Refs 2, 6,
12, 13, 25, 27, 32, 33.
Indian Pond-Heron Ardeola grayii (Huvadhoo raabodhi). A. g. grayii; A.
g. phillipsi. (In 1 993, L. Isdhoo, two on 1 4 November. It is not known if these
were migrant nominate grayii, of which there have been two previous
records further north in the archipelago, or an extension of range of the
resident race phillipsi, abundant on the two southerly atolls of Seenu and
20
J. S. ASH and ALI SHAFEEG
Forktail 10
Gaafu Alifu/Gaafu Dhaalu.) A. g. grayii is a straggler collected at Lhaviyani
Atoll, and three pond-herons reported at K. Vilingili in ii probably belong
here; phillipsi is confined to the southern atolls, where it is an abundant
resident. Breeding activity in x-ii. In addition recorded: Seenu and Gaafu
Alifu/Gaafu Dhaalu Atolls. Refs 2, 6, 12, 13, 25, 27, 28, 30, 33.
Striated Heron Butorides striatus (Dhivehi raabodhi). B. s. didii and B. s.
albidulus. (In 1984, one to three noted in April-May 1984 on K. Kurumba
Resort and K. Kan’doomaafushi; H. A. Dhidhdhoo and H. A. Maarandhoo
[Ash], In 1993, widely distributed with 54 individuals on M. Muli; L.
Maandhoo, L. Mendhoo, L. Kunahandhoo, L. Fares, L. Isdhoo, L. North
Athahedha, L. Vadinolhu, L. Maabaidhoo, L. Hurasdhoo; A. Feridhoo.
Presumably all didii, with many birds, especially on Laamu Atoll, being pale
grey to whitish.) Common resident throughout the archipelago, but
probably decreasing. B. s. didii is the race reported from the northern and
central atolls, while albidulus is reported to be confined to the southern. Also
recorded Kaafu Atoll: K. Male, K. Vilingili, K. Hulhule and K. Guraadhoo;
Seenu Atoll: S. Hithaadhoo and S. Gamu; Gaafu Alifu/Gaafu Dhaalu Atoll.
Breeds x-xi. Refs 2, 4, 6, 7, 8, 12, 13, 14, 20, 21, 22, 25, 26, 27, 33.
Black-crowned Night-Heron Nycticorax nycticorax (Raabodhi). (A bird
captured on Kaafu Atoll in 1 983 was photographed [Shafeeg] .) This is the
only record from the Maldives. Ref 32.
Yellow Bittern Ixobrychus sinensis (Dhonraabodhi). (A bird captured on
Seenu Atoll in 1 987 was photographed by Shafeeg.) A rare visitor recorded
twice on S. Meedhoo. Refs 25, 32, 33.
Cinnamon Bittern Ixobrychus cinnamomeus (Rathu raabodhi). (A bird
captured without details of date or locality was photographed by Shafeeg.)
An occasional visitor recorded about four times; once on Toddu Islet, west
of K. Male and three times on Seenu Atoll in iii, viii, x, xii. Refs 2, 25, 27,
32, 33.
Black Bittern D upetorjlavicollis (Ka\hu raabodhi). D.f. flavicollis. Infrequent
visitor with about four records of 1-3 birds, i, iii, iv, xii. Also recorded: K.
Male and K. Vilingili; Seenu Atoll twice. Refs 25, 27, 33.
Great Bittern Botaurus stellaris (no local name). A rare vagrant seen on
three days, x-xii, on S. Gamu. Refs 25, 33.
Greater Flamingo Phoenicopterus ruber (Gudu gudaa dhooni) . (One caught
Haa Alifu Atoll, undated, was photographed [Shafeeg].) Ahamed Shafeeg
states that it occurs sporadically and that it is well-established in local
folklore. Ref 32.
Glossy Ibis Plegadis falcinellus (Kalhu bulhi thubi). Rare visitor to S. Gamu
in i and x. Refs 2, 25, 33.
Eurasian Spoonbill Platalea leucorodia (Dheyfai dhooni). Twice caught in
Vaavu Atoll, according to Ahamed Shafeeg, once in the 1950s and again in
1984. Ref 32.
1994
Birds of the Maidive Islands
21
Great White Pelican Pelecanus onocrotalus (Hudhu girubaa dhooni). (An
adult captured in Shaviyani Atoll in 1974 was brought to Male and
photographed [Shafeeg].) Ahamed Shafeeg reports observing two in 1962.
Ref 32.
[Spot-billed Pelican Pelecanus philippensis (Alhigirubaa dhooni). Ahamed
Shafeeg reports this as a rare visitor, with a maximum of five together, the
first two observed in 1962. However, no details are available. Ref 32.]
Great Frigatebird minor (Maa hoara). A frequent visitor, recorded
1, v, vi, xii, from K. Male; Seenu Atoll; Gaafu Alifu Atoll; L. Hithadhoo; Baa
Atoll; Gnyaviyani Atoll. Refs 2, 3, 25, 27, 31, 33.
Lesser Frigatebird Fregata ariel (Hoara). F. a. iredalei. (In 1993, Vattaru
Channel, one on 5 November. M. Mulah, two on 9 November; L.
Maandhoo, one on 10 November and two on 11 November, L.
Kunahandhoo, one on 1 2 November, L. Maabaidhoo, two on 1 5 November.)
Plentiful around most atolls and probably resident on some. Breeding x and
xi (ref 14). Also recorded: B. Olhugin and B. Thulhaadhoo; Gaafu Alifu/
Gaafu Dhaalu Atoll; S. Gamu; Gnyaviyani Atoll. Refs 2, 3, 6, ?8, 12, 14,
25, 27, 31, 33.
Bulwer’s Petrel Bulweria bulwem (Hoagula). Very rare visitor: one on S.
Feydhoo in viii. Refs 2, 9, 24, 25, 33.
Wedge-tailed Shearwater Puffinus pacificus (Bodu hoagulhaa). (One off
Sh. Maaugoodhoo on 30 April 1984 [Ash]). A frequent visitor, sometimes
plentiful, iii-vii. Also recorded between Seenu and Gaafu Dhaalu Atolls.
Frequents adjoining sea areas, iv-x. Refs 2, 4, 25, 27, 31, 33.
Flesh-footed Shearwater Puffinus cameipes (Maa hoagulhaa). (One
captured 26 May 1982, K. Male was photographed [Shafeeg].) Small
numbers in the south, iii-v, vii and x, in the Equatorial Channel between
Seenu and Gaafu Dhaalu Atolls, and dozens in July 1991 in the channels
between Laamu and Thaa and between Thaa and Dhaalu (R. C . Anderson) .
Refs 2, 3, 11, 15, 25, 27, 31, 33.
Audubon’s Shearwater Puffinus Iherminieri (Dhivehi hoagulhaa). P. 1.
bailloni (P. /. persicus according to ref. 14). (Two between Shaviyani and
Noonu Atolls, 30 April 1984; two, one and one between Shaviyani and
Kaafu Atolls, 6 May 1984 [Ash], Two birds captured at K. Male in 1983,
were photographed [Shafeeg], In 1993: off M. Raiymandhoo, two on 5
November; M. Kureli, one on 9 November; Dh. Dhoores, two heard,
probably this species (A. M. Hutson). Stated to breed on Meemu Atoll, on
all small islands from M. Kolhufushi north-east to M. Raiymandhoo.) A
frequent and widespread visitor, sometimes in large numbers, but possibly
decreasing; breeds xii-ii, perhaps throughout the year. Also recorded: great
numbers bred Lh. Dhiffushi and Lh. Olhuvelifushf reported to breed on G.
A. Hithaadhoo; observed in small numbers in the Equatorial Channel. Refs
2, 3, 4, 6, 9, 14, 18, 25, 27, 31, 32, 33.
22
J. S. ASH and ALI SHAFEEG
Forktail 10
Wilson’s Storm-Petrel Oceanites oceanicus (Kadukabaa). (In 1993, one
flew south off Faafu Atoll on 16 November; a late bird.) Large numbers
occur iv-x in the seas surrounding the atolls. Refs 6, 25, 27, 31, 33.
White-faced Storm-Petrel Pelagodroma marina (no local name). Very
rare visitor: one found dead Seenu Atoll in vii, and one seen in the 1°°
Channel in August 1994 (R. C. Anderson). Ref 3, 33.
White-bellied Storm-Petrel Fregetta grallaria (no local name). One
definite and a probable in the 1° Channel in August 1994 (R. C. Anderson).
No previous record from the Maldives. Ref 3.
Rufous-tailed Shrike Lanius isabellinus (no local name). A rare visitor
recorded only in 1975 on Seenu Atoll. Ref 33.
Brown Shrike Lanius cristatus (no local name). A winter visitor with about
six records, xi-i on S. Gamu. Refs 2, 25, 33.
House Crow Corvus splendens (Kaalhu). C. s. maledivicus. (The endemic
subspecies is now absent from many islands in the central Maldives,
following the government’s former policy, now rescinded, for its total
extermination as a major pest of fruit and cereal crops and in fish-drying
procedures. It was noted as follows, with some estimated populations in
1 984 in parentheses: K. Kan’doomaafushi (16), K. Guraadhoo (16) and K.
Gaafaru; Lh. Hinnavaru (200); N. Huivani; Sh. Firubaidhoo; H. Dh.
Kuburudhoo; H. A. Dhidhdhoo (?250), H. A. Thakandhoo and H. A.
Vashafaru (?100); H. Dh. Kumundhoo; Sh. Lhaimagu. Several were
feeding newly fledged young in the northern atolls in early May 1984.
Crows commuted over c. 10 kms of sea between H. A. Dhidhdhoo and H.
A. Vashafaru [Ash], In 1993, K. Biyaadhoo, two on 4 November and four
on 5 November; M. Midi, 20 on 5 and 6 November, and two carrying
nesting material on 8 November; M. Boahuraa, one on 5 and 6 November;
M. Mulah, 27 on 8 November; L. Maamendhoo, 20+ on 10 November, L.
Maandhoo, 100 on 10 November, L. Hithadhoo, three on 12 November,
L. Mendhoo, four on 12 November, L. South Athahedha, three on 13
November, L. Fares, 15 on 13 November, L. Vadinolhu, one on 13
November, L. North Athahedha, four plus on 13 November, L. Isdhoo, 30
on 14 November, L. Maabaidhoo, 200 on 15 November. Dhaalu Atoll:
small islet, one on 15 November; Dh. Dhoores, one on 15 November; Dh.
Ribudhoo, five on 1 5 November. A. Feridhoo, 30+ on 1 7 November.) With
the above exceptions it is resident and abundant throughout the archipelago
except in Seenu Atoll and the islands from which it has been removed
recently. Breeds i, iv-ix, xii, and probably all months. Also recorded: K.
Vilingili and K. Male , Gaafu Alifu/Gaafu Dhaalu Atoll. Refs 2, 4, 5, 6, 13,
14, 19, 21, 22, 25, 27, 28.
Eurasian Golden-Oriole Oriolus oriolus (no local name). Rare passage
migrant with two records on Seenu Atoll in x. Ref 33.
1994
Birds of the Maidive Islands
23
Asian Paradise flycatcher Terpsiphone paradisi (no local name). Two
records in x and xi on S. Gamu. Refs 2, 25, 33.
Eyebrowed Thrush Turdus obscurus (no local name). (A bird captured at
M. Musaru in 1 983 was photographed [Shafeeg] .) This is the only record
for the Maldives. Refs 4, 32.
Indian Robin Saxicoloides fulicata (no local name). One record in xi on
Seenu Atoll. Ref 33.
Northern Wheatear Oenanthe oenanthe (no local name). One record in x
on Seenu Atoll. Ref 33.
Pied Wheatear Oenanthe pleschanka (no local name). Irregular winter
visitor with six records on S. Gamu, x-xii. Refs 2, 25, 33.
Isabelline Wheatear Oenanthe isabellina (no local name). A fairly regular
autumn visitor, with eight records, x-xii, on S. Gamu. Refs 2, 25, 33.
Common Starling Stumus vulgaris (no local name) . One on Seenu Atoll in
i. Refs 2, 17, 25, 33.
Common Myna Acridotheres tristis (Mainaa) . This species became established
on K. Male through the release of cage-birds prior to 1939. The population
of c.200 died out during World War II during a period of acute local food
shortage (Ahamed Shafeeg). Only one record since, on K. Vilingili, in spite
of the statement that it is well established in the Maldives (Ali and Ripley
1987). Refs 2, 13, 32.
Sand Martin Riparia riparia (Forikey) . A regular winter visitor and passage
migrant, ix-xi and v on S. Gamu. Refs 25, 33.
Plain Martin Riparia paludicola (Forikey) . One record in xi on Seenu Atoll.
Ref 33.
Barn Swallow Hirundo rustica (Forikey). H. r. gutturalis. A northern winter
visitor annually, ix-ii, in small numbers. Reported: K. Male, K. Vilingili; S.
Gamu; Gnyaviyani Atoll. Refs 2, 3, 13, 14, 22, 25, 27, 33.
Northern House-Martin Delichon urbica (Forikey). (One, H. A.
Maarandhoo, on 4 May 1984. It soon attracted the company of six House
Crows, with which it played in elaborate aerobatics for at least half an hour.
Identification as D. urbica, rather than Asian House-Martin D. dasypus, is
claimed with confidence [Ash] .) Irregular winter visitor, x-ii, sometimes in
moderate numbers. Also recorded: K. Male and K. Hulhule; S. Gamu.
Refs 2, 4, 12, 14, 23, 25, 27, 33.
[Warbler Phylloscopus (no local name). One recorded on Seenu Atoll in x
was considered by the observer to be a Willow Warbler P. trochilus, but this
seems very unlikely to be correct, given that there is only one record for the
species from the Indian subcontinent. Ref 33.]
House Sparrow Passer domesticus (Gay kurulla, a Singhalese name). (One
to three seen often in two sites in K. Male in April and May 1 984. The males
had a broad black throat line above a conspicuously large black breast patch.
24
J. S. ASH and ALI SHAFEEG
Forktail 10
and had a striking call rendered as a plaintive ‘schweet’ [Ash].) Ahamed
Shafeeg observed the establishment of this species in K. Male, which
commenced in 1962 when a local resident began to release surplus birds he
was rearing in captivity. This was continued over the years, leading to the
build-up of a large resident population, which was augmented by c. 1 00 birds
that arrived with a grain ship from Sri Lanka in around 1980. This
population was almost entirely exterminated by a German rodent control
team in around 1981, but it is now building up again with a present
population of c.200 mainly based in the port area. There are no other
records from the Maldives. Ref 4, 32.
Yellow Wagtail Motacilla flava (Fenfoa dhooni). Irregular winter visitor
in small numbers, x-xii, and sometimes iii-iv, probably mainly on passage,
on K. Male, S. Gamu and once on a ship 72 kms south of Seenu Atoll. Refs
2, 12, 25, 27, 33.
Grey Wagtail Motacilla cinerea (no local name). Two records of single
northern migrants in xi and xii on S. Gamu. Refs 2, 25, 33.
Tree Pipit Anthus trivialis (Dhonfenfoah dhooni). A. t. trivialis. One record
of a single bird in xii on K. Male. Refs 2, 25, 27.
Red-throated Pipit Anthus cervinus (Mushi fenfoah dhooni). Autumn
passage migrant and winter visitor in small numbers recorded at least five
times, ix-xii, on K. Male and S. Gamu. Probably an annual visitor. Refs 2,
25, 27, 33.
Special thanks are due to Mr Ahamed Shafeeg, Director of the Council for Research on Maldivian
History and Culture, for making his collection of photographs available for examination, and for
valuable notes and discussion. We are especially grateful to Tim Inskipp who exceeded his normal
editorial roll over the presentation and lay-out of the paper, and spent much invaluable time in helping
to disentangle both difficult photographic identification problems and the complexity of atoll and
island names. Dr W. R. P. Bourne also looked at all the seabird photographs to check on our
identifications, and provided much useful comment. The Minister of Agriculture, M. V. Maniku
provided help and much kind hospitality, and others who helped and assisted in various ways included
Ms Aisha, Dr R. C. Anderson, Abdul Hameed Ali, A. A. Azeez, J. Belien, P. R. Colston, Dr C. J.
Feare, L. Fiedler, Ali Rasheed, Ibrahim Rasheed, and Ismail Shiyam. Dr. Nigel Collar provided
much editorial assistance, and both he and David Bishop traced some literature. Sue Wells resolved
many problems concerning the names of islands and atolls, and helped over the loan of photographs
during her visit to Male in 1989. The introduction to the Appendix is almost entirely hers, with some
additional information from Dr R. C. Anderson. Dr C. P. J. Ash kindly drew the map.
REFERENCES
1. Anon. (1979) Map of Maldives. Male: Novelty' Printers and Publishers.
2. Ali, S. and Ripley S. D. (1987) Compact edition of the handbook of the birds of India and Pakistan.
New Delhi: Oxford University Press.
3. Anderson, R. C. (1990-1994) Personal observations.
4. Ash, J. S. (1984a) Personal observations, 1984.
1994
Birds of the Maidive Islands
25
5. Ash, J. S. (1984b) Vertebrate pest management (Pest and crow control). Report prepared for the
Government of the Republic of the Maldives. Rome: FAO (TCP/MDV/2307).
6. Ash, J. S., Howard, R. and Moore, A. (in prep.) Bird observations and recommendations for bird
conservation. Pp. 24-28 in M. Holmes, A. M. Hutson and J. M. Morris, eds. The Maldives
Archipelago, Indian Ocean. A report on an investigation of fruit bats and birds, November
1993.
7. Bangs, O. (1913) The Green Heron of the Maldives. Proc. Biol. Soc. Washington 26: 93-94.
8. Bourne, W. R. P. (1966) Observations on islands in the Indian Ocean. Sea Swallow 18: 40-43.
9. Bourne, W. R. P. (1967) Long distance vagrancy in the petrels. Ibis 109: 141-167.
10. Bourne, W. R. P. (197 1) The birds of the Chagos group, Indian Ocean. Atoll Res. Bull. 149: 175-
207.
11. Chapman, S. E. (1982) Notes on seabird reports received 1980-1981. Sea Swallow 31: 5-24.
12. Duncan, J. (1973) The birds of Gan. R.A.F. Om. Soc. Newsletter 19: 4-7.
13. Fitter, R. S. R. (1981) A note on the birds of the Maidive Islands. Bull. Brit. Om. Club 101 ■ 386-
387.
14. Gadow, H. and Gardiner, J. S. (1903) Aves. Pp. 368-373 in J. S. Gardiner, ed. The fauna and
geography of the Maidive and Laccadive Archipelagoes , 1. Cambridge: Cambridge University
Press.
15. Gill, F.B. (1967) Observations on the pelagic distribution of seabirds in the western Indian
Ocean. Proc. U.S. Nat. Mus. 123: 1-33.
16. Harrison, P. (1983) Seabirds: an identification guide. Beckenham: Croom Helm.
17. Jany, E. (1957) Star ( Sturnus vulgaris ) uberquert die Arabische See. Vogelwarte 19: 140-142.
18. Jouanin, C. (1970) Note taxinomique sur les petits puffins, Puffinus Iherminieri, de l’Ocean
Indien occidental. Oiseau el R.F.O. (5)40: 303-306.
19. Meyer, P. (1980) About a 2-days result of crow eradication in Hinnavaru and at Naifaru from
the 24th to 25th March 1980. Unpublished report to Ministry of Agriculture, Maldives.
20. Morris, R. O. (1963) The birds of some islands in the Indian Ocean. Sea Swallow 16: 68-79.
21. Moutou, F. (1985a) Briefly: the Maidive Islands. Oryx 19: 232-233.
22. Moutou, F. (1985b) Les lies Maldives. Le Courrier de la Nature 96: 29-33.
23. Phillips, W. W. A. (1958) Notes on the nesting of the Blacknaped Tern Sterna sumatrana
mathewsi Stresemann in the Maidive Islands. J. Bombay Nat. Hist. Soc. 55: 567-569.
24. Phillips, W. W. A. (1959) Note on the occurrence of Bulwer’s Petrel Bulweria bulwerix in the
Indian Ocean. Bull. Brit. Om. Club 79: 100-101.
25. Phillips, W. W. A. (1963) The birds of the Maidive Islands, Indian Ocean. J. Bombay Nat. Hist.
Soc. 60: 546-584.
26. Phillips, W. W. A. and Sims, R. W. (1958a) Two new races of birds from the Maidive
Archipelago. Bull. Brit. Om. Club 78: 51-53.
27. Phillips, W. W. A. and Sims, R. W. (1958b) Some observations on the fauna of the Maidive
Islands, 3. Birds. J. Bombay Nat. Hist. Soc. 55: 195-217.
28. Reichenow, A. ( 1 904) Uebersicht der auf der deutschen Tiefsee Expedition gesammelten Vogel .
Wissenschaftliche Ergebnisse der deutschen Tiefsee-Expedition auf dem Dampfer ‘Valdivia’ 1898-
99 7: 345-358.
29. Salvadori, T. and Giglioli, E. H. (1889) Uccelli raccolti durante il viaggio della corvetta Vettor
Pisani negli anni 1879, 1880 e 1881. Mem. Reale Accad. Sci. Torino (2)39: 99-143.
30. Scheer, G. (1960) Eine neue Rasse des Teichreihers Ardeola grayii (Sykes) von den Malediven.
Senck. Biol. 41: 143-147.
31. Shafeeg, Ahmed (1988) [Sea birds in the Maldives.] ? (In Maldivian.)
32. Shafeeg, Ahamed. Personal notes and photographs.
33. Strickland, M. J. and Jenner, J. C. (1978) A report on the birds of Seenu Atoll (Maidive
Islands). J. Bombay Nat. Hist. Soc. 74: 487-500.
J. S. Ash, Godshill Wood, Fordingbridge, Hampshire, SP6 2LR, U.K.
Ali Shafeeg, Ministry of Fisheries and Agriculture, Male 20-05, Republic of Maldives.
26
J. S. ASH and ALI SHAFEEG
Forktail 10
Figure 1. The Maidive Islands
1994
Birds of the Maidive Islands
27
APPENDIX 1
NAMES OF MALDIVIAN ATOLLS
Each atoll generally has two names: an older ‘geographical’ name referring to the atoll feature, and a newer ‘code’
name referring to the administrative unit. There are 26 natural atolls but only 19 administrative units - some units
cover two atolls, but some of the large atolls are divided into two units (the capital Male is regarded as a twentieth).
The two systems are equally correct and both are current at present. However, the code name is becoming increasingly
popular and is used particularly by younger people. Some atolls seem to be known regularly by their code name (e.g.
Dhaalu), others by their geographical name (e.g. Alifu). There seem to be no rules as to which name system is used,
except that they should not be mixed. One authority is said to use geographical names for scientific papers, whilst
another apparently uses the code name because it is simpler. The code system is named after the Maldivian alphabet,
and the atolls are named from north to south. There is enormous variation in spelling, presumably because it is not
necessarily clear how to transcribe the Maldivian script into our alphabet (the presence or absence of ‘u’ at the end
of a word is particularly variable).
A third, separate, naming system is based on the latin alphabet (‘letter’ in the list below). Administrative units are
assigned letters from A to S starting from the north; Male town is assigned the letter T. This system is used for a few
special applications, for example in boat registrations.
Atholhu is atoll , Uthuruburi is north part and comes after the name, and ‘Dhekunuburi’ is south part and also
comes after the name; however, the English names are used below. The spellings used are from an island and atoll
compendium currently being compiled by Hassan Maniku. Atoll code names (in italics in the left hand column) are
used in the systematic list. A cross reference to all synonyms is provided in the following list.
Geographical names and synonyms
Seenu
Ari, Rasdu and Thoddu
part of Alifu
Malosmadulu South & Goifulhafehendhoo
Nilandu South
Nilandu North
Lhaviyani
part of Vaavu
Gnyaviyani
part of Kaafu
Huvadu (Suvadiva) North
Huvadu (Suvadiva) South
Fuvah Mulaku
part of Baa
Tiladunmathi North & Ihavandhippolhu
Tiladunmathi South & Makunudu
Laamu
Goifulhafehendhoo
Gaafu Alifu & Gaafu Dhaalu
part of Haa Alifu
Male North and South, Kaashidoo & Gaafaru
part of Kaafu
Thaa
Haddunmati
Faadhippolu
part of Haa Dhaalu
part of Kaafu
Raa
part of Baa
28
J. S. ASH and ALI SHAFEEG
Forktail 10
* Italicised names are the present code names which are
alongside each one). All the atolls lie close to 73°E.
Mulaku
Shaviyani
Noonu
Meemu
Faafu
Dhaalu
Miladunmadulu South
part of Kaafu
Malosmadulu North
part of Alifu
Addu
Miladunmadulu North
part of Kaafu
Gaafu Alifu
Gaafu Dhaalu
Kolumadulu
Haa Alifu & Haa Dhaalu
part of Alifu
part of Haa Alifu
part of Haa Dhaalu
Felidu & Vattaru
part of Vaavu
on the Maldivian alphabet (its relevant letters are shown
1994
Birds of the Maidive Islands
29
APPENDIX 2
List of islands mentioned in the text
The names conform as far as possible with the Map of Maldives (ref 1). Alternative spellings used in the cited references
are also given, with the reference numbers given in parentheses.
Aligaa (Lhaviyani Atoll)
Bandos (Kaafu Atoll)
Baresdhoo (Laamu Atoll)
Bibera (Haa Alifu)
Biyaadhoo (Kaafu Atoll)
Boahuraa (Meerau Atoll)
Bodufaru (Raa Atoll)
Bodufmolhu (Laamu Atoll)
Bodulhaimendhoo (Noonu Atoll) = Bodu Mandu (14)
Bushy Islet (Seenu Atoll) unnamed on map, = Kaduhira, Kanda Hera (23)
Dhagathi (Alifu Atoll) = Dugati
Dhidhdhoo (Haa Alifu Atoll) = Didhoo
Dhiffushi (Kaafu Atoll) = Diffuri (27)
Dhiffushi (Lhaviyani Atoll) = Difuri (14, 30)
Dhigufinolhu (Kaafu Atoll)
Dhoonidhoo (Kaafu Atoll) = Dunidu (27)
Dhoorcs (Dhaalu Atoll)
Eboodhoo (Kaafu Atoll) = Embudu
Eydafushi (Baa Atoll) (14, 27) = Hedufuri
Fahala (Thaa Atoll)
Fares (Laamu Atoll)
Feridhoo (Alifu Atoll)
Feydhoo (Seenu Atoll) = Fedu (24)
Filladhoo (Haa Alifu Atoll)
Firubaidhoo (Shaviyani Atoll) = Firubaidoo
Fonadhoo (Laamu Atoll)
Foojaadi (Kaafu Atoll) = Fujarde (27)
Foah Mulah (Gnyaviyani Atoll) = Fuah Malok, Furah Mulaku, Fua Malaku
Fulhadhoo (Baa Atoll) = Furudu (14)
Funadhoo (Shaviyani Atoll) = Furnadu (14, 27)
Furannafushi (Kaafu) = Furunafushi, Foran Fushi
Gaafaru (Kaafu Atoll) = Gaha Faro, Garo Faro
Gamu (Seenu Atoll) = Gan (12, 25, 27, 33)
Gardu Islet (Kaafu Atoll) (27) = ?Gaadhoo
Grawa (Kaafu Atoll) = PGiraavaru
Gulhi (Kaafu Atoll)
Guraadhoo (Kaafu Atoll) = Guraidhoo, Guraidoo
Hibalhidhoo (Baa Atoll) = Hebaridu (14)
Himmafushi (Kaafu Atoll) = Himmafuffi (27), Hima Fushi
Hinnavaru (Lhaviyani Atoll)
Hithaadhoo (Baa Atoll) = Hithadhoo, Hittadu (20, 23), Hitadu (30)
Hithaadhoo (Gaafu Alifu Atoll)
Hithadhoo (Laamu Atoll)
Huhlimendhoo (Laamu Atoll)
Huivani (Noonu Atoll)
Hulhule (Kaafu Atoll) = Hulule (26, 27)
Hulhudhoo (Seenu Atoll) = Huludu (14)
Hurasdhoo (Alifu Atoll) = Harasdhoo
Isdhoo (Laamu Atoll) = Isdu
Kadhdhoo (Laamu Atoll) = Kaddhoo, Kadhu
Kagi (Kaafu Atoll)
Kalhaidhoo (Laamu Atoll)
Kadholhudhoo (Raa Atoll) = Kandoludhoo
Kan’doomaafushi (Kaafu Atoll) = Kadoomaa Fushi, Kudumaa Fushi
Kaashidhoo (Kaafu Atoll) = Kaasidoo
Kassanfaru (Kaafu Atoll) = Kahsanfaru, Cassanfaru (27), Cassanfarra (27)
30
J. S. ASH and ALI SHAFEEG
Forktail 10
Kedhikolhu (Noonu Atoll) = Kendikolu (14)
Kolhufushi (Meemu Atoll)
Kuburudhoo (Haa Dhaalu Atoll) = Kuburudoo
Kudafares (Laamu Atoll)
Kumundhoo (Haa Dhaalu Atoll) = Kumundoo
Kunahandhoo (Laamu Atoll) = Koonahandhoo
Kureli (Meemu Atoll)
Kurumba Resort (N.Male Atoll) = Vihamanaafushi (?) Wihamanafushi, Weehammanarfurri (27),
Wehammanarfurri (27)
Landhoo (Noonu Atoll) = Landu (14)
Lankanfinolhu (Kaafu Atoll)
Lankanfushi (Kaafu Atoll) = Lankeumfurii (27), Lankconfurri (18)
Lhaimagu (Shaviyani Atoll) = Lhoimagu
Lhosfushi (Kaafu Atoll)
Limbo kandu (Raa Atoll) (14)
Maaugoodhoo (Shaviyani Atoll) = Maa Ugudu
Maabaidhoo (Laamu Atoll)
Maafahi (Haa Alifu Atoll)
Maafushi (Kaafu Atoll) = Maagushi
Maahaa Reef (Kaafu Atoll)
Maakadoodhoo (Shaviyani Atoll)
Maamendhoo (Laamu Atoll)
Maamendhoo (Seenu Atoll) = Maradu (14, 20)
Maandhoo (Laamu Atoll)
Maarandhoo (Haa Alifu Atoll) = Marandhoo
Maavah (Laamu Atoll) = Maarah
Mabaru (Baa Atoll)
Madoovari (Baa Atoll) = Maduwari (14)
Male (Kaafu Atoll)
Medhufinolhu (Kaafu Atoll) = Minueofinol (27)
Meedhoo (Seenu Atoll) = Medu (25), Midu (14)
Mendhoo (Laamu Atoll)
Mulah (Meemu Atoll)
Muli (Meemu Atoll)
Musaru (Meemu Atoll)
Naifaru (Lhaviyam Atoll)
N. Athahedha (Laamu Atoll)
Olhugiri (Baa Atoll) = Olugeri (14)
Olhuvelifushi (Lhaviyani Atoll) = Olivelifuri (14)
Omadhoo (Thaa Atoll) = Omadhu
Othuveli (Laamu Atoll)
Raiymandhoo (Meemu Atoll)
Ribudhoo (Dhaalu Atoll)
S. Athahedha (Laamu Atoll)
Thaburudhoo (Kaafu Atoll) = Tambrudu (27)
Tern Islet (Seenu Atoll) (unnamed on map)
Thakandhoo (Haa Alifu Atoll) = Takandhoo
Thulhaadhoo (Baa Atoll) = Thulhaadho, Tuladu (27), Turadu (14)
Thulhaagiri (Kaafu Atoll) = Thulhagiri, Tulargiri (27)
Thundudhoshu (Laamu Atoll) = Thundudhoshu Finolhu
Toddu Islet (Kaafu Atoll) (27)
Ukulhas (Alifu Atoll) = Ukuthas
Utheemu (Haa Alifu Atoll)
Vadinolhu (Laamu Atoll)
Vashafaru (Haa Alifu Atoll) = Washafaru
Vattaru (Noonu Atoll) = Wataru
Vilingili (Kaafu Atoll) = Villingili, Viligili, Willingillie (27)
Vilufushi (Thaa Atoll)
Ziyaaraifushi (Laamu Atoll)
1994
Birds of the Maidive Islands
31
APPENDIX 3
CONSERVATION OF BIRDS IN THE MALDIVES
In order to conserve the wildlife, environment and natural beauty of the archipelago for the benefit of posterity, several
ear y decisions and actions require to be undertaken by the Government of the Republic of the Maldives. Following
a visit with the Bat Conservation Trust by the three undersigned ornithologists to the Maldives in November 1993
and by one of us with an FAO project in 1 984, we propose the following recommendations for consideration regarding
1 . It is suggested that an experienced expatriate conservation/wildlife adviser should visit the Maldives for a period
of up to one year to work with the government’s personnel in drawing up a conservation management policy and
plan for the whole archipelago.
2. What appears to be a major and widespread market in birds between the atolls and Male, involving the import
of birds from abroad, and the dispatch of birds from other atolls to Male, needs to be fully investigated and
assessed. It seems now to have reached a stage where possibly all seabirds of some species are being destroyed
in the Maldives, and urgent legislation is required for their protection and to prevent their total loss
3. As in many other countries, e.g. Seychelles, New Zealand, etc., breeding colonies of seabirds are an important
tourist attraction being visited by increasing numbers of ‘ecotourists’. Early action should be taken to survey and
record all known present and previous breeding sites throughout the Maldives as a basis for an action plan. The
importance of seabirds as indicators of fish presence is, of course, well-known.
4. Establish an educational conservation-awareness programme throughout the atolls, in collaboration with the
conservation/ wildlife adviser. This should be directed principally through the schools, but be supported by radio
talks, television programmes, lecture tours, etc.
5. Before much international support or recognition can be expected the Maldives needs to provide convincing
proof that it is serious in its intent to protect its wildlife and environment. At an early stage support should be
received for a conservation/wildlife adviser through international aid and conservation agencies (e.g. WWF,
IUCN, EC, RSPB, etc.). Effective action would do much to further the Maldives’ image overseas, and also attract
the increasing number of conservation-minded tourists.
6. Other potential sources of support and funding might include the following: the introduction of a ‘conservation
tax of, say, 3-5% on all tourists’ bills; Shell Chemicals through an environmental impact study following their
seismic survey; various airlines serving the Maldives; the resort islands themselves, etc.
7 . Restrictions will need to be imposed on the use by tourists of uninhabited islands in the neighbourhood of resorts.
The establishment of reserves, or protected islands, could commence immediately, but in the first place should
be confined to selected islands already known to hold breeding colonies of seabirds, or feeding areas for
shorebirds. Public access to breeding colonies on relatively small islands needs to be controlled very carefully.
8. The marketing of birds could cease almost totally and immediately through the suppression of the bird market
in Male, the prevention of the resort islands being used as potential marketing channels (apparently currently
being undertaken in connection with live lobster transfers), and through directives to Atoll chiefs to the
communities under their control, particularly with regard to the wholesale capture of fledgling seabirds.
9. An on-site training programme could be developed by the conservation/wildlife adviser. Early thought also should
be given towards appropriate training overseas for a Maldivian Wildlife officer and a Conservation Education
Officer. It would obviously be of value for the national Wildlife Officer if a tour was arranged to the Seychelles
or elsewhere to study the methods employed in their system of wildlife tourism management.
10. The presence of House Crows presents a problem on some islands. Where some control becomes necessary, an
ecological approach to the problem is recommended. Suppression of their numbers could be greatly controlled
by an improvement in sanitary conditions and better organised garbage disposal - both of which at present
probably provide much of the birds’ diet. An attempt is needed to suppress numbers to an acceptable level, rather
than their total elimination.
11. There may be a need to seek alternative activities for the many people currently involved in bird persecution.
Many might be required as bird-guides in tourism, and as wardens or guards on protected islands.
J. S. Ash
R. Howard
A. Moore
November 1993
Forktail 10
1994
FORKTAIL 10 (1994): 33 - 48
33
The Avifauna and Conservation Value of
Shey-Phoksundo National Park, Nepal
ANDERS PRIEME and BO 0KSNEBJERG
Shey-Phoksundo National Park is the only protected area in the trans-Himalayan region of Nepal
and, covering 3,555 km-, it is the country’s largest national park. The 38 species recorded within the
national park for which Nepal may hold significant world populations are listed, together with a
complete list of the 1 78 species recorded within the park to date. A summary of the main vegetation
types within the park is provided, as well as an account of the conservation value and ornithological
importance of each vegetation type. An account of the use of the park by people is given, and
management problems in the park are described.
Shey-Phoksundo National Park (S.P.N.P.) is located in the Dolpa and
Mugu districts of western Nepal, between 28°58'-29056’N and 82°35'-
83°14E. Covering 3,555 km2, S.P.N.P. is the largest national park in Nepal.
It was gazetted in 1984 to preserve a variety of unspoilt trans-Himalayan as
well as Himalayan habitats, along with the protection of a number of
endangered mammal species such as the Snow Leopard Panthera uncia,
Grey Wolf Canis lupus, and Himalayan Musk Deer Moschus chrysogaster.
The national park is divided in two by the Kanjiroba Himal which
reaches its highest point at the 6,883 m Kanjiroba South Peak. About one-
third of the park is situated south of Kanjiroba Himal and encompasses
habitats typical of the Himalaya with extensive high-altitude grasslands
interspersed with forests and scrubberies below 4,000 m. The habitats
include forests of oak and conifers, mixed deciduous forests, and shrubberies
of rhododendron and Cotoneaster. Here, the landscape is often extremely
rugged even by Nepalsese standards making survey work everything from
breathless to dangerous.
North of Kanjiroba Himal the landscape changes dramatically. The
steep hillsides of the true Himalaya are replaced by the gentle undulating
hills of the Tibetan plateau. Because the Kanjiroba Himal acts as a rain
barrier, the northern part of the national park only receives sparse rainfall.
This is reflected in the vegetation, which is typical for a trans-Himalayan or
Tibetan steppe and near desert vegetation, dominated by Caragana and
dwarf junipers Juniperus.
34
ANDERS PRIEME and BO 0KSNEBJERG
Forktail 10
■N.
KEY: | _ |
[R] = Ranger Post; [HQ] = National Park Headquarters I I
0 20km
Figure 1. Shey-Phoksundo National Park, Nepal
1994
The avifauna and conservation value of Shey-Phoksundo National Park
35
PREVIOUS ORNITHOLOGICAL WORK IN SHEY-
PHOKSUNDO NATIONAL PARK
Parallel to his botanical achievements Oleg Polunin was the first to make
ornithological records in what is now Shey-Phoksundo N.P. (Polunin
1952). From his descriptions of birds seen during his 1952 expedition to
Dolpo it is evident that he saw at least 42 species in the area covered by the
park, including several bird species new to Nepal, three of which are of
Tibetan affinity: Tibetan Partridge Perdix hodgsoniae , Little Owl Athene
noctua , and Tibetan Ground-Jay Pseudopodoces humilis (Inskipp and Inskipp
1991). Robert L. Fleming, Jr. was the next to contribute to the ornithological
knowledge of Dolpo during his visit to this remote region in June 1971
(Fleming 1975, 1982). He noted 100 species in the area of the park,
including 73 not recorded by Polunin. Dr George B. Schaller and Peter
Matthiessen visited the area in October-December 1973 mainly to study
Bharal Pseudois nayaur; the former mentioned six species of birds in his book
Stones of silence (Schaller 1980) and the latter mentioned 16 species in his
book The Snow Leopard (Matthiessen 1978). Rodney M. Jackson worked in
the Namlang valley between December 1976 and February 1977 and
recorded 55 species of birds, including 15 new for the park area (Jackson
1978). He returned there several times from 1981 to 1985 with Darla
Hillard, and they added three new species to the list (Hillard 1989). Dr
Pralad Yonzon surveyed the western part of the national park in 1991 and
his list (Yonzon 1991), which raised the park list by 15 species to a total of
152, indicated that additional ornithological work was needed in the park.
Between 27 March and 17 May 1992 we made a survey of the southern
part of the national park (Prieme and Dksnebjerg 1992). The area surveyed
included Jagdula Khola, Garpung Khola, along Suli Gad River and areas
near Shey Gomba (Fig. 1). Besides work on the distribution of Snow
Leopard and Bharal, botanical inventories, and human activity in the park,
we investigated the bird species in all areas visited. A total of 1 25 bird species
was found including 26 species new to the park, bringing the total recorded
there to 178.
CONSERVATION VALUE
Shey-Phoksundo National Park is the only protected area in Nepal
representative of the trans-Himalayan region. The park is of great importance
for nature conservation not only in Nepal, but also in the Indian subcontinent,
mainly because of its large size and low level of human disturbances. The
extensive high-altitude grasslands within the park are the home of a sizeable
and viable population of Snow Leopard together with good numbers of
major herbivores, of which the Bharal is the most common.
36
ANDERS PRIEME and BO 0KSNEBJERG
Forktail 10
Table 1. Bird species recorded within Shey-Phoksundo National Park for which Nepal may have
significant world populations according to Inskipp and Inskipp (1986) and Inskipp (1989).
1 2
Snow Partridge Lerwa lerwa
Himalayan Monal Lophophorus impejanus
Wood Snipe Gallinago nemoricola
Speckled Wood- Pigeon Columba hodgsonii +
Himalayan Woodpecker Dendrocopos himalayensis +
Rufous-breasted Accentor Prunella strophiata
Robin Accentor Prunella rubeculoides
Indian Blue Robin Luscinla brunnea +
Golden Bush-Robin Tarslger chrysaeus
White-browed Bush-Robin Tarsiger indicus +
Blue-fronted Redstart Phoenlcurus frontalis
White-throated Redstart Phoenicurus schisticeps
White-bellied Redstart Hodgsonlus phoenicuroldes
Plain-backed Thrush Zoothera mollisslma +
Tickell’s Thrush Turd us unicolor
White-collared Blackbird Turdus albocinctus ? ?
Grey-sided Bush-Warbler Cettia brunnifrons
Grey-hooded Warbler Seicercus xanthoschistos +
Large-billed Leaf-Warbler Phylloscopus magnirostris +
Buff-barred Warbler Phylloscopus pulcher +
Rusty-tailed Flycatcher Muscicapa ruficauda (+)
Ultramarine Flycatcher Ficedula superciliaris +
Yellow-bellied Fantail Rhipidura hypoxantha + +
Variegated Laughingthrush Garrulax variegatus
Green Shrike-Babbler Pteruthius xanthochloris +
White-browed Fulvetta Alcippe vinipectus
White-throated Tit Aegithalos niveogularis +
Grey-crested Tit Parus dichrous
Rufous-vented Tit Parus rubidlventris +
Black-crested Tit Parus melanolophus +
White-cheeked Nuthatch Sitta leucopsis
Kashmir Nuthatch Sitta cashmirensis +
Grey-backed Shrike Lanius tephronotus
Pink-browed Rosefinch Carpodacus rodochrous +
White-browed Rosefinch Carpodacus thura
Streaked Rosefinch Carpodacus rubicilloides
Red-headed Bullfinch Pyrrhula erythrocephala + +
Collared Grosbeak Mycerobas affinis ?
Key Vegetation type:
1 = Mixed deciduous forest
2 = Oak/conifer forest
3 = Himalayan scrub
4 = Himalayan alpine meadows
5 = Trans-Himalayan habitats
3
(+)
+
?
+
(+)
?
+
+
+
+
+
+
+
+
+ = Recorded in the vegetation type and probably breeds there
(+)= Recorded in the vegetation type but not known to breed there
? = Recorded within N.P. most likely in the indicated vegetation type
4 5
?
+ +
+
+
+
+
+
+
+
+
1994
The avifauna and conservation value of Shey-Phoksundo National Park
37
The park has a good variety of forests, many of which are of high quality.
Even though these forests only comprise a minor fraction of the total area
coveied by the national park, about 59% of the bird species recorded, and
65 /o of breeding or probably breeding species depend on forests or scrub
(throughout the rest of this paper the term ‘breeding species’ includes those
known to breed as well as those assumed to breed).
Breeding bird species currently recorded from Shey-Phoksundo National
Park number 137 and more are likely to be found. There are 1 24 bird species
for which Nepal may hold significant proportions of the world populations,
as their breeding distributions are restricted to an area encompassing the
Himalaya, north-east India, northern South-East Asia and south-west
China (Inskipp and Inskipp 1986, Inskipp 1989). As many as 38 of these
(31 /o of the total) have been recorded within S.P.N.P., and a majority of
these has been proved or are assumed to breed within the park (Table 1).
Nepal may be especially important for 36 breeding bird species because
they either have particularly restricted ranges within the general area under
consideration or have been described as uncommon or rare in the Indian
subcontinent (Inskipp and Inskipp 1986, Inskipp 1989). Two of these have
been recorded within the park: Wood Snipe Gallinago nemoricola, whose
breeding status in the park is unknown, and White-throated Tit Aegithalos
niveogularis, which is common and presumably breeds in the national park.
Also, the Wood Snipe is listed as a breeding species at risk in Nepal (i.e. at
a national level) (Inskipp 1989) and is recognised as internationally threatened
(Collar and Andrew 1988).
The avifauna and conservation value of the major vegetation types within
the park are described below. Table 2 lists for each type: numbers of
breeding species, and numbers of breeding species with significant world
populations in Nepal.
Table 2. Bird species proved or presumed to breed within Shey-Phoksundo National Park.
Key 1 = Number of breeding species
2 = Number of breeding species with significant world populations in Nepal
3 = % breeding species with significant world populations in Nepal
38
ANDERS PRIEME and BO 0KSNEBJERG
Forktail 10
Mixed, deciduous forest:
Mixed deciduous forests are found along the Suli Gad River between 2,700
and 3,500 m. At their best these forests are luxuriant with a wealth of tree
species and a well developed understorey of bushes and saplings. Even
though this vegetation type covers only a minor fraction of the total national
park area, the number of breeding bird species compares favourably with
that of other vegetation zones (Table 2). Future surveys in this vegetation
type are likely to add more species to the park list, especially if done in late
spring or early summer. Also, future surveys are likely to reveal that these
forests are the most species-rich of all habitats within the park.
The high proportion of 29% of the total number of breeding species in this
vegetation type may have significant world populations in Nepal. The most
notable of these is the White-throated Tit.
Oak! conifer forest:
This vegetation type encompasses several different forest types and is
named oak/conifer forest for simplicity. These different forests are similar
in that they dominate below 3,900 m in most valleys in the Himalayan part
of the national park. Exceptions are along the Suli Gad River where mixed
deciduous forests dominate, in the vicinity of villages where forests have
given place to cultivated land, and slopes with a southerly aspect presumed
to be too dry to support forests. The forest type that dominates in a specific
area is determined mainly by altitude and aspect.
The most prominent forest type consists of oak Quercus semecarpefolia
mixed with different conifers typical of West Nepal like West Himalayan
Spruce Picea smithiana , Himalayan Silver Fir Abies spectabilis, and Himalayan
Blue Pine Pinus wallichiana. The forests vary from pure stands of oak to pure
coniferous forests. Many of the forests are in excellent condition while
others, mainly near villages, are affected by firewood collecting, by lopping
for fodder (of Quercus semecarpefolia ), and by domestic goats and yaks
grazing the understorey. In Jagdula Khola we observed forest degradation
mainly near trails. Further than 40-60 m from man-made trails the forests
are usually only affected by grazing, presumably when herds of yaks and
goats are taken to and from traditonal grazing grounds, and to a small extent
by firewood collection. It is not possible from a single study to estimate the
rate of forest degradation, but we have a feeling that the present rate is rather
low in most of the areas we surveyed.
Forests of Himalayan Birch Benda edulis (3, 1 00-3,900 m) are common in
Jagdula Khola and Garpung Khola. These forests are not badly affected by
degradation, but some of them are badly infested with snare traps. The traps
are made by local people, mainly to catch Himalayan Musk Deer and
Himalayan Monal Lophophorus impejanus. The traps are operated from late
spring until well into autumn when herders attending their herds of yaks and
1994
The avifauna and conservation value of Shey-Phoksundo National Park
39
goats are near the remote birch forests. It is estimated that the trapping is
likely to take a heavy toll on local populations of Musk Deer and Himalayan
Monal.
Shrubberies of rhododendron Rhododendron are found only on some
hillsides with a northerly aspect and hence a more humid microclimate.
Rhododendrons are far less common in S.P.N.P. compared to localities
further east in Nepal.
As many as 36% of the breeding bird species in these forest types may have
significant world populations in Nepal. Notable species are Himalayan
Monal (Nepal’s national bird) which despite trapping is a common sight in
many birch forests, Green Shrike-Babbler Pteruthius xanthochloris , and two
species with a limited distribution in the western Himalaya, the White-
throated Tit and White-cheeked Nuthatch Sitta leucopsis.
Himalayan scrub:
The scrublands in the Himalayan part of the national park mainly consist
of Cotoneaster and, in some places, of Caragana, as between Sumduwa and
Ringmo.
Only 21 of the total number of species found within the park are likely
to breed in this habitat. This low figure is partly due to the fact that
scrublands in most places only cover relatively small areas, and partly to the
fact that some scrublands, especially in the vicinity of traditional grazing
grounds for livestock, are burned more or less regularly. Burning is not
permitted within the park but is practiced to some extent by local people to
enlarge existing grazing grounds.
The most exciting observation in this habitat was of two Wood Snipes
flushed from low Cotoneaster scrub near a meandering stream in Pani Palta
Khola. The species is scarce in Nepal (Inskipp and Inskipp 1991) though it
has been recorded recently (Buckton and Morris 1993). The two birds were
observed on 1 2 April, too early in the year to decide if they had only stopped
on migration or intended to breed in Pani Palta Khola, where presumably
suitable habitat exists.
Himalayan alpine meadows:
The extensive high-altitude meadows are a major asset of the national park.
Compared to elsewhere in Nepal the meadows within S.P.N.P. are often in
excellent condition, and they are the home of the Snow Leopard and its
major prey the Bharal. Bharals are often seen in flocks numbering several
dozens, while the secretive Snow Leopard is only seen on very rare
occasions, even by local herders.
Despite the generally optimistic view of the condition of the meadows in
the park, intense grazing by domestic yaks and goats is taking place in several
areas, e.g. in Pani Palta Khola 260 yaks were crowded in the lower part of
40
ANDERS PRIEME and BO 0KSNEBJERG
Forktail 10
the valley. The herders had taken the yaks the two-week-walk from the
village of Saldang in the eastern part of the park to Pani Palta Khola, due to
deteriorating grazing grounds near Saldang.
Intense grazing is likely to displace wild herbivores, as has presumably
happened in Pani Palta Khola. Here the resident Bharals were only seen on
the steep hillsides bordering the valley and never in the fertile valley bottom
where the yak herd was grazing.
The birds classified as breeding in this habitat include a number of species
which actually breed in nearby forests or on cliffs but depend on the
grasslands for foraging. These include the Golden Eagle Aquila chrysaetos
and Common Kestrel Falco tinnunculus, which feed on the abundant small
and medium-sized mammals. The Upland Buzzard Buteo hemilasius may
breed in S.P.N.P. but has not yet been proved to breed in Nepal.
Trans-Himalayan habitats:
About two-thirds of S.P.N.P. is situated north of the Himalaya proper. Here
Tibetan or trans-Himalayan steppe and near-desert vegetation dominate,
though some areas are virtually denuded of any vegetation. Large areas are
wilderness areas with minimal human influence and with viable populations
of Snow Leopards and Grey Wolves.
The avifauna shows a heavy influence from Tibet. Many of the species
recorded in S.P.N.P. are widespread in Tibet but have a very limited
distribution within Nepal like the Tibetan Partridge, Hill Pigeon Columba
rupestris, Little Owl, Hume’s Lark Calandrella acutirostris , Brown Accentor
Prunella fulvescens, White-browed Tit-Warbler Leptopoecile sophiae, Tibetan
Ground-Jay, and Black-winged Snowfmch Montifringilla adamsi. The great
influence from the Tibetan avifauna makes it less surprising that only five
species presumed to breed in this part of the park have a significant part of
the world population in Nepal.
USE OF THE PARK BY PEOPLE AND MANAGEMENT
PROBLEMS
About 2,000 people inhabit the villages scattered around the park. They
practice subsistence farming based on livestock and growing mainly barley
and potatoes. Living conditions in this harsh region are extremely rough,
and the people of the northern villages only survive due to a century-old
system of trading salt from the highlands of Tibet with grain from the
Nepalese middle hills.
The number of people living inside the park is supplemented with people
who move into the park with their livestock from the surrounding villages
1994
The avifauna and conservation value of Shey-Phoksundo National Park
41
in late April and May and remain until early autumn. During this period
herders live in rock caves or tents on the grazing grounds.
In at least some villages, e.g. Hurikot just outside the park, livestock
numbeis have increased substantially in recent years. Though we did not
observe any seriously degraded meadows during our survey, some grazing
grounds appeared to be heavily grazed by livestock. Intensified grazing
might have a considerable impact on these meadows; just south of the park
we observed several landslides and an abundance of erosion gullies cut
through the landscape.
The forests of S.P.N.P. are exploited far less than many others in Nepal.
This is mainly because the park lies in the country’s least populated zone.
Not surprisingly, forests near villages are affected by firewood collection,
but the high number of soldiers within the park, especially the 150 troops
at Sumduwa Army Checkpost present a special problem because they take
a toll on the nearby forests. The Department of National Parks and Wildlife
Conservation (DNPW C) has started negotiations with the proper authorities
to reduce the number of soldiers. The latter are a heavy burden on the
DNPWC annual budget (the Department’s financial allocation for 1990/
1991 is NRs 142.3 million of which 84% is for protection units from the
Royal Nepal Army (IUCN 1992)).
Hunting, mostly with traps, is taking place in Jagdula Khola (Prieme and
0ksnebjerg 1 992) and Namlang Khola in the north-western part of the park
(Jackson 1979). Two types of traps, snares and poisoned bamboo spears, are
used. The snares are usually found in narrow strips of high-altitude birch
forest and are intended for Himalayan Musk Deer, the musk glands of which
are worth a small fortune to local farmers. Also, Himalayan Monal and,
occasionally, Common Goral Naemorhedus goral are trapped. Elaborate
barriers made of branches and twigs cover the full width of the forest strips,
making passage possible only through gates in the barriers where the snares
are set. The poisoned bamboo spears are usually placed in very steep terrain
near rivers or streams which Bharal and Goral frequent. The 60-100 cm
long spears hidden in the vegetation are tipped with poison made from
aconites Aconitum and can kill a full-grown Bharal weighing 40 kg or a Snow
Leopard in a few minutes. Interviews with hunters inside and outside the
park indicated the existence of a ‘Tibetan connection’ for wildlife products
originating in western Nepal. Apparently, hunters are paid in advance by
Tibetan traders for valuable products like gall bladders from Himalayan
Black Bear Selenarctos thibetanus (fetching prices of NPs 9,000), and musk
glands from Musk Deer. The Tibetans sell these products together with
pelts from Snow Leopards and the bones from all major carnivores to
Chinese working in Tibet who reportedly hope to make a profit when
returning to a major Chinese city (e.g. Jackson 1991).
Until May 1989, S.P.N.P. was off-limit to foreigners. At that time the
42
ANDERS PRIEME and BO 0KSNEBJERG
Forktail 10
Himalayan part of the national park was opened to tourists. In 1990 35
foreign tourists visited the national park. This number rose to 291 in 1991 .
As yet, tourism has not had a great impact on the park, but the number of
tourists visiting the park is expected to rise substantially in future years.
However, S.P.N.P. is remote even by Nepalese standards and tourism here
will never reach the level of the most popular destinations in Nepal like
Khumbu, the Annapurna region or Langtang. At present the park authorities
are doing a fine job trying to keep tourist groups at special campsites while in
the park. This substantially reduces the impact of tourist groups. Visitors to
the park are required to be self-sufficient in fuel supplies but park regulations
allow trekking crews to gather dead wood from the forest floor. To the best
of our knowledge, no study on the impact of wood gathering has been
carried out in Himalayan forest ecosystems. It is possible that intense wood
gathering will change the number and diversity of insects and birds which are
dependent on a rich forest floor litter. Another problem with wood gathering
is that the borderline between dead wood and live wood is easily crossed. On
several occasions we observed trekking crews cutting down branches of live
trees and up-rooting entire live bushes for fuelwood or campfires.
Our major concern regarding tourism within S.P.N.P. is the recently
opened trans-Himalayan part of the park. With its unique blend of Buddhist
culture and remote wilderness, this part of the park acts like a new ‘Shangri-
La’ on many foreign tourists visiting Nepal. Having becoming famous
through Peter Mathiessen’s novel. The Snow Leopard, the monasteries and
the scenery at Shey are especially appealing to western tourists. But the
trans-Himalayan habitats are extremely fragile and vulnerable to even a
small number of tourists. Trees are very rare in this desert-like area and the
regeneration of the Curagarca/juniper scrub is exceedingly slow. Also, the
large and conspicuous trekking groups might have disturbing effects on the
shy Snow Leopard, and on its prey the Bharal. At present, Bharal can be
approached within 5-20 m at Shey. Hopefully, the current high trekking fee
for visiting Shey will restrain the number of tourists.
It is not within the scope of the present study, nor is it within our academic
capacity, to investigate the socio-economic impact of tourism in the park,
but it is likely that a steady flow of tourists will have a great impact on the
culture and economy of the remote villages in the northern part of the
national park. However, everything seems to have its own pace in Dolpo
and, despite anticipated increases in numbers of livestock and tourists,
S.P.N.P. will probably have untouched wilderness areas for years to come.
The birds of S.P.N.P. are still inadequately studied throughout the year, so
birdwatchers surveying at any season are likely to make valuable observations.
Surveys in spring to locate breeding and wintering species of the lower
forests would be especially worthwhile. Anyhow, the visiting birdwatcher
will be rewarded with several western Himalayan and Tibetan specialities
1994
The avifauna and conservation value of Shey-Phoksundo National Park
43
which are difficult to see elsewhere in Nepal, along with the feeling of being
in Snow Leopard territory - you never know when their flaming eyes are
watching you.
We are grateful to His Majesty’s Government of Nepal which gave its support to the project. We owe
special thanks to Dr. T. Maskey, Director General of the Department of National Parks and Wildlife
Conservation, for his encouragement and valuable support. Also, special thanks go to Mr. Lai Bihari
Yadav, Chief Warden in S.P.N.P., to Senior Game Scout Sakka B. Rokaya, Game Scout Dhayr, and
Game Scout Dawa Tenzing, for their participation in the field work and for being excellent travel
companions. Many persons and institutions helped us to carry out the project and they are all thanked
- but Carol and Tim Inskipp deserve warm thanks for their never-ending support. Tim Inskipp is also
thanked for valuable improvements to the manuscript. The field work of the project was supported
by World Wide Fund for Nature - Denmark, due to a generous donation from the Beckett
Foundation.
REFERENCES
Ali, S. and Ripley, S. D. (1983) Handbook of the birds of India and Pakistan. Compact edition. New
Delhi: Oxford University Press.
Buckton, S. T. and Morris P. A. J. (1993) Observations of Wood Snipe Gallinago nemoricola in Nepal.
Oriental Bird Club Bulletin 17: 31-35.
Collar, N. J. and Andrew, P. (1988) Birds to watch. The ICBP world checklist of threatened birds.
Cambridge, U.K.: International Council for Bird Preservation (Techn. Publ. no. 8).
Fleming, R. L., Jr. (1975) Liste des oiseaux du district de Dolpo (Reng-Pungmo), Tichurong et
Dolpo. Pp. 449-452 in C. Jest, Dolpo, communautes de langue tibetaine du Nepal. Paris: Editions du
Centre National de la Recherche Scientifique.
Fleming, R. L., Jr. (1982) List of birds recorded in Dolpo district in 1971. Unpublished.
Hillard, D. (1989a) Vanishing tracks. London: Elm Tree Books.
Hillard, D. (1989b) Notes on birds recorded in Nepal, 1982-1985. Unpublished.
Inskipp, C. (1989) Nepal’s forest birds: their status and conservation. Cambridge, U.K.: International
Council for Bird Preservation (Monograph no. 4).
Inskipp, C. and Inskipp, T. (1986) Some important birds and forests in Nepal. Forktail 1: 53-64.
Inskipp, C. and Inskipp, T. (1991) H guide to the birds of Nepal. Second edition. London: Christopher
Helm.
IUCN (1992) Protected areas of the world: a review of national systems. Volume 1: Indomalaya, Oceania,
Australia and Antarctica. Gland, Switzerland and Cambridge, U.K.: International Union for
Conservation of Nature and Natural Resources.
Jackson, R. (1978) A report on wildlife and hunting in the Namlang (Langu) valley of west Nepal.
Unpublished report to National Parks and Wildlife Conservation Office, Kathmandu.
Jackson, R. M. (1979) Aboriginal hunting in West Nepal with reference to musk deer, Moschus
moschiferus moschiferus, and snow leopard, Panthera uncia. Biol. Conserv. 16: 63-72.
Jackson, R. M. (1991) Snow leopards and other wildlife in Qomolangma Nature Reserve of Tibet.
Snow Line 9(1): 9-12.
Mathiessen, P. (1978) The Snow Leopard. New York: Viking Press.
Polunin, O. (1952) Notes on birds recorded in Nepal, 1952. Unpublished.
Prieme, A. and Oksnebjerg, B. (1992) Field study in Shey-Phoksundo National Park. Report to
Department of National Parks and Wildlife Conservation, Kathmandu. Unpublished.
Schaller, G. B. (1980) Stones of silence. New York: Viking Press.
Yonzon, P. (1991) Avifauna of Shey-Phoksundo National Park. Unpublished.
Anders Prieme and Bo Oksnebjerg, c/o WWF -Denmark, Ryesgade 3F, 2200 Copenhagen N, Denmark.
44
ANDERS PRIEME and BO 0KSNEBJERG
Forktail 10
APPENDIX
A COMPLETE LIST OF BIRDS RECORDED IN
SHEY-PHOKSUNDO NATIONAL PARK
A = This survey
F = Fleming (1975, 1982)
H = Hillard (1989a and b)
J = Jackson (1978)
M = Mathiessen (1978)
P = Polunin (1952)
S = Schaller (1980)
Y = Yonzon (1991)
FHJ
A HJ
AFHJ P
AFHJM
FHJ
Y
A JP
H
A
S
A
A
F
A
F
Y
J
J
AF
AF
J
J
A
F M
AF JMP
AFHJM PS
AF Y
A P
Snow Partridge Lerwa lerwa Uncommon resident.
Tibetan Snowcock Tetraogallus tibeianus Uncommon in Himalayan part of N.P.
Himalayan Snowcock Tetraogallus himalayensis Common around Shey and some other areas.
Chukar Alectoris chukar Resident.
Tibetan Partridge Perdix hodgsoniae Resident in trans-Himalayan habitat.
Koklass Pheasant Pucrasia macrolopha Resident.
Himalayan Monal Lophophorus impejanus Common in some areas like Jagdula Khola.
Bar-headed Goose Anser indicus
Ruddy Shelduck Tadoma ferruginea
Tufted Duck Aythya fuligula Uncommon visitor.
Himalayan Woodpecker Dendrocopos himalayensis Resident.
Scaly-bellied Woodpecker Picus squamatus Resident.
Eurasian Hoopoe Upupa epops
Little Green Bee-eater Merops orientalis One seen on 1 6 April 1992 near Toijam Rangerpost at 2,900
m in clearing in oak forest. This is the highest altitude for the species in Nepal (Inskipp and Inskipp
1991). The bird had probably ‘overshot’ on spring migration as 16 April falls within the migration
period of the species (Inskipp and Inskipp 1991). Also, see notes about Large-tailed Nightjar.
Common Cuckoo Cuculus canorus
Lesser Cuckoo Cuculus poliocephalus
Himalayan Swiftlet Collocalia brevirostris
Alpine Swift Tachymarptis melba
Common Swift Apus apus Fairly common around e.g. Shey.
Tawny Owl Strix aluco Common in forest in Himalayan part of N.P.
Little Owl Athene noctua
Short-eared Owl Asia flammeus
Large-tailed Nightjar Capnmulgus macrurus A single individual seen on 1 April 1992 at 3,100 m in
mixed oak/pine forest above Toijam Rangerpost. This is the highest altitude record for the species in
Nepal (Inskipp and Inskipp 1991). Though the species is found up to 2,200 m in the western Himalaya
and 2,400 m in north-eastern India (Ali and Ripley 1 983), this individual had probably ‘overshot’ while
migrating. This is not the only lowland species recorded at an unusually high altitude within the
national park: this study also found a Little Green Bee-eater Merops orientalis at 2,900 m, and Robert
L. Fleming, Jr. (Fleming 1982) recorded a Hair-crested Drongo Dicrurus hottentottus at 4, 1 00 m, both
of them probably after a spring migration ‘overshoot’.
Rock Pigeon Columba livia
Hill Pigeon Columba rupestris Common around Shey.
Snow Pigeon Columba leuconota Common in most areas.
Speckled Wood-Pigeon Columba hodgsonii Only along Suli Gad River.
Oriental Turtle-Dove Streptopelia orientalis Common in Himalayan part of N.P.
1994
The avifauna and conservation value of Shey-Phoksundo National Park
45
A
Common Crane Grits grus Migrant.
A
Y
A
F P
AFHJMPS
F
AFHJM
A J
AF J
A J
AF
A Y
Y
AF JM
A
AFHJ P
FJ
J
A
A P
F P
AF
A JMP
A HJ P
AFHJMP
AFJMPS
AFH
AF
Y
F
AF
AF JM
A
FHJ
AFH P
A
A
P
A HJ
FJ
AF Y
A
A Y
AF Y
F Y
Y
AF J P
A P
AF
F
Common Coot Fulica atra
Wood Snipe Gallinago nemoncola Two flushed from scrub near stream on 12 April 1 992 in Pani Palta
Khola at 4,100 m. The species is listed as a breeding species at risk in Nepal by Inskipp (1989), and
there are only very few recent records of the species in Nepal (Inskipp and Inskipp 1991). The species
is also recognised as internationally threatened (Collar and Andrew 1988).
Ibisbill Ibidorhyncha struthersii A single individual noted on 14 April in Pani Palta Khola at 3,800 m
feeding along a small stream.
Black-eared Kite Milvus lineatus
Lammergeier Gypaetus barbatus Common resident in most areas.
Egyptian Vulture Neophron percnopterns
Himalayan Griffon Gyps himalayensis Common resident in most areas.
Northern Harrier Circus cyaneus Uncommon winter visitor.
Eurasian Sparrowhawk Accipiter nisus Not known if resident or a migrant.
Northern Goshawk Accipiter gentilis Not known if resident or a migrant.
Common Buzzard Buteo buteo
Upland Buzzard Buteo hemilasius Resident.
Steppe Eagle Aquila nipalensis Migrant.
Golden Eagle Aquila chrysaetos Common resident in several areas.
Booted Eagle Hieraaetus pennatus Uncommon summer visitor.
Common Kestrel Falco tinnunculus Common in most areas.
Amur Falcon Falco amurensis Uncommon migrant.
Merlin Falco columbarius Uncommon winter visitor.
Long-tailed Shrike Latiius schach
Grey-backed Shrike Lanius tephronotus
Tibetan Ground-Jay Pseudopodoces humilis A trans-Himalayan resident.
Spotted Nutcracker Nucifraga caryocatactes
Red-billed Chough Pyrrhocorax pyrrhocorax
Yellow-billed Chough Pyrrhocorax graculus Common.
Large-billed Crow Corvus macrorhynchos Common below 4,000 m.
Common Raven Corvus corax Resident.
Long-tailed Minivet Pencrocotus ethologus Common below 3,500 m.
Yellow-bellied Fantail Rhipidura hypoxantha Common in e.g. Jagdula Khola.
Ashy Drongo Dicrurus leucophaeus
Hair-crested Drongo Dicrurus hottentottus Uncommon visitor.
White-throated Dipper Cinclus cinclus
Brown Dipper Cinclus pallasii
Chestnut-bellied Rock-Thrush Monticola rufiventris
Blue Rock-Thrush Monticola solitarius
Blue Whistling-Thrush Myiophoneus caeruleus Common below 4,100 m.
Plain-backed Thrush Zoothera mollissima
Tickell’s Thrush Turdus unicolor
White-collared Blackbird Turdus albocinctus
Dark-throated Thrush Turdus ruficollis
Mistle Thrush Turdus viscivorus
Dark-sided Flycatcher Muscicapa sibirica
Rusty-tailed Flycatcher Muscicapa ruficauda
Rufous-gorgeted Flycatcher Ficedula strophiata
Ultramarine Flycatcher Ficedula superciliaris
Slaty-blue Flycatcher Ficedula tricolor
Verditer Flycatcher Eumyias thalassina
White-tailed Rubythroat Luscinia pectoralis Common at e.g. Shey.
Indian Blue Robin Luscinia brunnea Common along Suli Gad River.
Orange-flanked Bush-Robin Tarsiger cyanurus Common in forests between 2,900 m and 4,000 m.
Golden Bush-Robin Tarsiger chrysaeus
46
ANDERS PRIEME and BO 0KSNEBJERG
Forktail 10
Y
A
AH P
AF MP
A
AF J
A J
AF P
AFHJ P
AF
AF
A P
FJ
AF P
AF Y
AF
H
F
F P
AH P
A
AF
AF JMP
AF
AF P
A HJ P
A P
A Y
A
AFH P
AFH P
AF Y
AF
Y
A Y
A J
Y
F
F
A
AFH
AFH
A
F Y
AF
AF
AF
A Y
AH Y
F
AF Y
AFH?
A J P
A
White-browed Bush-Robin Tarsiger indicus
Rufous-backed Redstart Phoenicurus erythronotus Uncommon winter visitor.
Blue-capped Redstart Phoenicurus caeruleocephalus Common below 3,600 m.
Black Redstart Phoenicurus ochruros Common in some places, e.g. near Shey.
Hodgson’s Redstart Phoenicurus hodgsoni Probably only an uncommon migrant.
White-throated Redstart Phoenicurus schisticeps Uncommon resident?
White-winged Redstart Phoenicurus erythrogaster Resident.
Blue-fronted Redstart Phoenicurus frontalis Common in most areas.
White-capped Water-Redstart Chaimarromis leucocephalus Common.
Plumbeous Water-Redstart Rhyacomis fuliginosus Uncommon.
White-bellied Redstart Hodgsonius phoenicuroides Found in the trans-Himalayan part of the park.
Grandala Grandala coelicolor Resident.
Little Forktail Enicurus scouleri Uncommon resident.
Siberian Stonechat Saxicola maura Common near Shey.
Grey Bushchat Saxicola ferrea
Desert Wheatear Oenanthe deserti Uncommon in trans-Himalayan habitats.
Brahminy Starling Stumus pagodarum
Kashmir Nuthatch Sitta cashmirensis Uncommon resident.
White-cheeked Nuthatch Sitta leucopsis Resident.
Wallcreeper Tichodroma muraria
Eurasian Treecreeper Certhia familiaris Resident.
Bar-tailed Treecreeper Certhia himalayana Common resident.
Winter Wren Troglodytes troglodytes Common below 4,500 m.
Dark-grey Tit Parus rufonuchalis
Rufous-vented Tit Parus ntbidiventris Common resident.
Black-crested Tit Parus melanolophus Common resident.
Grey-crested Tit Parus dichrous
Green-backed Tit Parus monticolus Resident.
Black-throated Tit Aegithalos concinnus Uncommon resident.
White-throated Tit Aegithalos niveogularis Common in forests below 3,800 m.
Eurasian Crag-Martin Hirundo rupestris Common in most areas.
Asian House-Martin Delichon dasypus Common in most areas.
Goldcrest Regulus regulus
Himalayan Bulbul Pycnonotus leucogenys Only along Suli Gad River.
Black Bulbul Hypsipetes leucocephalus Only along Suli Gad River.
Striated Prinia Prinia criniger
Oriental White-eye Zosterops palpebrosus
Brownish-flanked Bush-Warbler Cettia fortipes
Grey-sided Bush-Warbler Cettia brunnifrons
Booted Warbler Hippolais caligata Uncommon migrant.
White-browed Tit-warbler Leptopoecile sophiae A trans-Himalayan resident.
Tickell’s Leaf-Warbler Phylloscopus affinis Common around Shey.
Sulphur-bellied Warbler Phylloscopus griseolus Uncommon migrant.
Buff-barred Warbler Phylloscopus pulcher
Pale-rumped Warbler Phylloscopus chloronotus Common below 3,600 m.
Inornate (Yellow-browed) Warbler Phylloscopus inomatus Common below 3,600 m.
Greenish Warbler Phylloscopus trochiloides
Large-billed Leaf-Warbler Phylloscopus magnirostris
Blyth’s Leaf-Warbler Phylloscopus reguloides
Golden-spectacled Warbler Seicercus burkii
Grey-hooded Warbler Seicercus xanthoschistos
Streaked Laughing-thrush Garrulax lineatus Common resident in some areas.
Variegated Laughingthrush Garrulax variegatus Common resident in some areas.
Green Shrike-Babbler Pteruthius xanthochloris Uncommon resident.
1994
The avifauna and conservation value of Shey-Phoksundo National Park
47
AF
F
FJ
A J
AF P
Y
AF
F Y
J
AF P
F P
AF JM
AFH P
A
AFH
AF Y
AF
AY
AF J
A
AF JM
AF P
AF J
J
A
FJ
F M Y
FH
FJ
AF J S
AF J P
AF J
AF
AF Y
A
AF
F S
AFJ P
AF
P
AFJ
H
A J
AHJP
A
White-browed Fulvetta Alcippe vinipectus
Greater Short -toed Lark Calandrella brachydactyla
Hume’s Lark Calandrella acutirostris
Oriental Skylark Alauda gulgula
Horned Lark Eremophila alpesiris Common near Shey.
Fire-breasted Flowerpecker Dicaeum ignipectus
Mrs. Gould’s Sunbird Aethopyga gouldiae
Green-tailed Sunbird Aethopyga nipalensis
House Sparrow Passer domesticus
Russet Sparrow Passer rutilans
Eurasian T ree Sparrow Passer montanus
Black-winged Snowfinch Montifringilla adamsi A trans-Himalayan resident.
White Wagtail Motacilla alba Common in some areas.
Citrine Wagtail Motacilla citreola Migrant.
Grey Wagtail Motacilla cinerea
Olive-backed Pipit Anthus hodgsoni Common in e.g. Jagdula Khola.
Rosy Pipit Anthus roseatus Common on alpine meadows in most areas.
Upland Pipit Anthus sylvanus Uncommon.
Alpine Accentor Prunella collaris Common in several areas.
Rufous-streaked Accentor Prunella himalayana Uncommon winter visitor.
Robin Accentor Prunella rubeculoides Common near Shey.
Rufous-breasted Accentor Prunella strophiata Common in many areas between 3,500 m and 4,500 m.
Brown Accentor Prunella fulvescens Common near Shey.
Black-throated Accentor Prunella atrogularis Uncommon winter visitor.
Chaffinch Fringilla coelebs Uncommon winter visitor.
Fire-fronted Serin Serinus pusillus
Yellow-breasted Greenfinch Carduelis spinoides
European Goldfinch Carduelis carduelis
Twite Carduelis flavirostris
Plain Mountain-Finch Leucosticte nemoricola Common in open habitat.
Black-headed Mountain-Finch Leucosticte brandti
Common Rosefinch Carpodacus erythrinus
Beautiful Rosefinch Carpodacus pulcherrimus Common in many areas.
Pink-browed Rosefinch Carpodacus rodochrous
White-browed Rosefinch Carpodacus thura Uncommon.
Streaked Rosefinch Carpodacus rubicilloides Common at e.g. Shey.
Great Rosefinch Carpodacus rubicilla High-altitude resident.
Red-fronted Rosefinch Carpodacus puniceus A high-altitude resident. Common in some areas.
Red-headed Bullfinch Pyrrhula erythrocephala
Collared Grosbeak Mycerobas ajfinis Uncommon.
White-winged Grosbeak Mycerobas camipes
Spot-winged Grosbeak Mycerobas melanozanthos
Pine Bunting Emberiza leucocephalos An uncommon winter visitor.
Rock Bunting Emberiza cia Common.
Little Bunting Emberiza pusilla Uncommon winter visitor.
48
Forktail 10
1994
FORKTAIL 10 (1994): 49 - 64
49
Birds of Lakshadweep Islands
DEEPAKUMAR NARAYANA KURUP and V. J. ZACHARIAS
Lakshadweep archipelago supports a scanty avifauna with only two resident passerine species. On
Pitti there is a large breeding colony of Sooty Terns Sterna fuscata and Brown Noddies Anous stolidus.
Most of the atolls serve as staging grounds for a variety of shorebirds in winter. The uninhabited atolls
Suheli and Bangaram supported relatively richer avifaunas. Increased human population density
appeared to affect the ecology of most inhabited islands. Substitution of indigenous vegetation with
monoculture plantations and predation of tern eggs are among the factors limiting bird populations
in the islands.
Though Palaearctic migrants disperse widely during the northern winter, in
many of their wintering habitats, particularly certain island groups in the
central Indian Ocean, their status remains little studied. Lakshadweep, off
the west coast of Kerala is a regular staging ground for many shorebird
species. There have previously been brief accounts by Hume (1876),
Gadow and Gardiner ( 1 903), Ellis ( 1 924), Betts (1939) and Burton (1940);
also more recent reviews by Mathew and Ambedkar ( 1 964), Mohan ( 1989),
Anon. (1991) and Daniels (1992), but all of these previous accounts were
based on brief trips of less than a month duration. The present report is
based on a study carried out to assess and update the status of migrant and
resident birds in the archipelago. The study was conducted between 15
August 1985 and 31 July 1986 (and a few days in December 1988) in the
Union Territory of Lakshadweep. The observations were mostly carried out
on Kavaratti, the most centrally placed of the islands. Kavaratti is about the
same distance from the mainland as it is from the other islands of the
archipelago. Two heavily populated islands were not visited: Androth which
is probably the oldest in the Lakshadweep group and does not have the
typical reef-lagoon components of a coral atoll, and Chetlat, one of the
northernmost islands. All of the other inhabited islands, as well as the
majority of the uninhabited islets, were visited (Fig. 1), including the far-
flung isolated reefs of Baliapannium and Cheriyapannium, and also Perumal
Par, an uninhabited atoll with hardly any island interphase except for a
centrally placed reef flat. The duration of time spent in each island is given
in Table 1.
STUDY AREA
Lakshadweep is an archipelago of coral atolls, reefs and sandbanks. In all,
there are 36 islands and tiny islets situated between 8°N and 12°13’N and
between 71°E and 74°E. They lie about 220-440 km off the west coast of
Kerala. Most of the islands are widely separated from each other. In the
50
D. N. KURUP and V. J. ZACHARIAS
Forktail 10
Figure 1 . The Lakshadweep Islands
island group, cumulatively having a surface area of 32 km2, only ten are
inhabited: Kalpeni, Androth, Kavaratti, Amini, Kadmat, Agatti, Kiltan,
Chetlat, Bitra and Minicoy. Bitra is the smallest inhabited island. Though
the land area of the islands is small, the lagoon area is vast, with a total
surface area of 4,200 km2. Surrounding this are 20,000 km2 of territorial
waters and about 700,000 km2 of economic zone, thus making Lakshadweep
1994
Birds of Lakshadweep Islands, India
51
Table 1. Visits to islands of Lakshadweep
a truly large territory (Government of India 1985). Even during the
supposedly fair weather months the vagaries of the weather often make
travel between the islands difficult. All of the islands, except Androth,are
roughly crescent-shaped and have a north-south disposition . T o the east are
rocky beaches and to the west are the lagoons. The island Androth lies east
to west and has no lagoon. The surface of the islands lies at 1-4 m above
M.S.L. The islands have a warm and humid climate. The temperature
ranges between 25.4°C and 31 . 1°C. The annual rainfall varies between 151
cm and 164 cm, with most of it falling in June-August during the south-west
monsoon (Mannadiar 1977). The north-east monsoon is comparatively
weak and sets in during October-November. During much of this time, the
wind blows with a speed range of about 10 to 20 knots (18 to 40 km) from
the west and the sea becomes rough; surface communications between the
islands are then difficult. April and May are the hottest months. During the
rest of the period, from November to May, the weather is generally good and
52
D. N. KURUP and V. J. ZACHARIAS
Forktail 10
the sea is calm. The soil of the islands is calcareous and highly porous, being
derived from weathered coral boulders and shingles. Due to the high
percolation rate of the soil a quantity of rain water infiltrates underneath,
forming the ground water lens which floats over the denser saline water
underneath. The vegetation of all the islands is broadly similar. The
Coconut Cocos nucifera, which grows ubiquitously in most of the islands, is
a cultivated species. Among the wild flora, a laurel shrub Scaevola sericea,
Wild Heliotrope Toumefortia argentea, a bushy shrub Pemphis acidula and a
variety of other shrubs, including Lantana catnara, have been found.
Screwpine Pandanus tectorius has been found growing on a few islands such
as Minicoy and Bangaram. Ziziphus jujuba and Thespesia populnea have a
wide distribution. The ground vegetation consists of Spinifex littorens,
Commelina bengalensis etc. (Further details on the vegetation are given by
Sivadasan and Joseph 1981).
METHODS
The study was based on direct observations made while walking around the
islands, usually in the early morning or late afternoon, and during inter¬
island and island-mainland voyages in steamers and motor launches. A pair
of 7x30 binoculars was used. Although no trapping of birds was carried out,
many specimens could be physically examined after being noosed by local
children. Similarly, pet birds caught locally and kept in several individual
households were examined. Some of the field observations were documented
by photographs.
VISITS TO ISLANDS
Kavaratti, the third largest island in the Lakshadweep group, is the most
centrally placed island and is situated at 10°33’N 72°38’E, approximately
400 km west of Cochin. Quite typical of Lakshadweep islands, Kavaratti has
a north-south linear disposition and occupies the eastern rim of the
crescent-shaped atoll, with a lagoon to the west. The maximum length of the
island is 6 km and the breadth at its narrowest point is less than 100 m.
Except for a brief respite for a week or so in some months, observational data
on Kavaratti were collected right through the observation period. The
Oriental White-eye Zosterops palpebrosus was observed breeding from March
to May on Kavaratti. Seven abandoned nests were noted, made in small or
medium-sized trees and at heights varying from 4-5 m. Both the sexes
participated in nest-building, which in one case was noted as taking 6 h 10
mins, and the materials used were the fibres of coconut husk, cobwebs,
grizzled leaves and chicken-down.
1994
Birds of Lakshadweep Islands, India
53
Pitti (10°30’N 72°30’E). The tiny seabird island of Pitti (‘Pakshipitti’ as it
is locally known) which is 20 km north of Kavaratti, is an exposed reef, the
accessibility of which is almost always difficult. On our first visit to Pitti in
April 1986, repeated attempts to land were foiled because of bad weather;
however, after some time, an experienced islander did manage to swim
across to the islet and retrieved eggs of the Sooty Tern Sterna fuscata, Great
Crested Tern 5. bergii and Brown Noddy Anous stolidus. The exact number
of breeding birds could not be ascertained. On our second visit, in December
1988, the sea was calm enough for us to swim ashore and look at the birds.
Only Sooty Terns and Brown Noddies were present. Although there were
no hatchlings, eggs of both species were found. There were 5,000-6,000
Sooty Terns and 8,000-9,000 Brown Noddies. A total of 400 eggs was
found, two-thirds of which belonged to Sooty Terns. Large congregations
of the two species occurred side by side on the dry coral bed but were not
intermixed. Interestingly, Hume (1876) found nesting Sooty Terns and
Brown Noddies intermingled at Cherbaniani. The Pitti reef flat, though
teeming with birds for much of the year, appeared to be absolutely devoid
of any guano. It is probably because the reef, only 1.5-2 m above M.S.L.,
gets periodically rinsed by the surf from all sides. It is therefore puzzling to
see reports elsewhere about appreciable quantities of guano being found on
the islet (Mannadiar 1977). Pitti islet is nearly square in shape and is about
200 x 300 m in area. In early November 1985, young Sooty Terns were
noted on Kavaratti, having been brought by islanders from Pitti. Hume
failed to see any birds on Pitti island in late February 1876. Mathew and
Ambedkar (1964) collected young Great Crested Terns and Brown Noddies
in October, and they suggested that large numbers of both species nest on
the island between April and November every year and also that October
marks the end of the breeding season. On enquiry, most islanders asserted
that there is a peak in breeding activity during the south-west monsoon
period from June to August. Alcock (1902) saw the chicks of two types of
terns in November but he was unable to identify the species concerned. It
appears that there is an extended breeding period on Pitti, and it is also
probable that the terns have an irregular breeding cycle. However, a clear
picture has not emerged yet and the extent of breeding activity during the
monsoon needs to be ascertained. Especially noteworthy is the possibility of
an irregular breeding cycle of Sterna bergii in the tropical Indian Ocean as
conjectured by Feare (1979). The account in Anon. (1991) provides further
details of the breeding terns, with estimates of the total numbers present in
October 1963 (20,000), February 1978 (12,000), May 1990 (4,000),
February 1991 (2,000) and April 1991 (8,000), suggesting that there has
been a significant decrease in numbers in recent years.
Baliapannium (or Cherbaniani) is a large atoll, ‘oval shaped and about 6
miles by 2 " miles in its extreme dimensions’ as Hume (1876) described it.
54
D. N. KURUP and V. J. ZACHAR1AS
Forktail 10
Towards the northern extremity of the atoll is an islet some 200 m long and
50 m broad. The islet is very similar to Pitti in appearance, but is much more
accessible as it is within the lagoon, protected by the reef. The islet is devoid
of any vegetation and the substrate is littered with coral shingles and
boulders. Baliapannium was described as having a large breeding colony of
terns by almost all the authors who previously visited it. Both Hume and
Betts recorded Sooty Terns and Brown Noddies breeding there. Mathew
and Ambedkar collected Great Crested Tern eggs and Bridled Tern 5.
anaethetus nestlings. We, however, found Baliapannium devoid of any
breeding birds even on our second visit in April, 1986. There were flocks of
Ruddy Turnstones Arenaria interpres on the islet and large congregations of
Great Crested Terns and Lesser Crested Terns Sterna bengalensis on the
outlying sandbank. The absence of breeding birds could be due to the
sporadic incursions into the area by fisherfolk from Chetlat and Bitra. The
islanders, however, testified to some breeding activity on the islet during the
monsoon season, when the reef flat remains undisturbed.
Cheriyapannium (or Byramgore) was visited on 23 April 1 986. It is a very
large atoll, and at high water there is practically no land area exposed.
Except for a few terns S. bengalensis and 5. bergii, not many birds were
observed.
Perumal Par, an atoll situated south-west of Bitra, was visited on 24 April.
This atoll appeared very similar to Baliapannium, with an extensive lagoon.
Towards the south-eastern extremity of the reef is an exposed islet within the
lagoon. Here also, fishermen from the neighbouring islands make overnight
visits and, quite understandably, no birds were observed. However, two
large congregations of terns, most likely 5. bergii and 5. bengalensis were
observed a short distance north-east of the atoll. Large hunting flocks of
terns are a common feature in the neighbourhood of atolls and over different
parts of the sea between the islands. Flying-fish, an important prey of the
Tuna Euthynnus pelamis, are numerous and are caught by the terns.
Suheli atoll was visited twice, once in January 1986 and, later, in December
1 988. 5. bergii and 5. bengalensis were fairly numerous around the atoll. On
‘Suheli Pitti’, a 1 km long linear islet formed within the lagoon near the
north-eastern part of the reef, between Valiyakara and Cheriyakara, a flock
of S', bergii and S. bengalensis was found in almost equal proportions (Table
2). It was reliably learnt from the islanders that until five years ago, ‘Suheli
Pitti’ was used as a breeding ground by terns. No previous authors appear
to have described Suheli Valiyakara. ‘Suheli Par’ as it is also known, is south¬
west of Kavaratti and is situated at 10°05’N 72°18’E. It is the largest
uninhabited island and retains much of its natural vegetation. Suheli
1994
Birds of Lakshadweep Islands, India
55
Table 2. Estimates of tern populations in the different islands
Cheriyakara, the smaller island in the atoll, though devoid of any permanent
settlements, is replete with biotic activity for six months from mid-October
to mid-April. The waters around the atoll are rich in fishery resources and
men from Kavaratti and Agatti go to stay there and catch fish, which they
dry and produce ‘mas’. The ‘offal’ that is left over after the production of
mas provides good manure for coconuts, which thrive well. Valiyakara, on
the other hand, is virtually deserted though visited by people at least twice
a year for the collection of copra. Many of the coconut trees in Valiyakara
are retarded, but there is luxuriant ground vegetation. The vegetation,
particularly in the southern end of the island, is so thick that it is often
impenetrable. The ‘strand coral’ is composed of plants such as Scaevola
sericea, Pemphis acidula, Toumefortia argentea. Of all the islands, Suheli has
a greater representation of migrant and resident avifauna. The Grey Heron
Ardea cinerea is a resident found either singly or in pairs on most islands
visited. They were found in greater numbers where they bred on Suheli and
the Bangaram group of islands. The breeding season of the Grey Heron is
given by Ali and Ripley (1987) as from July to October in northern India and
from November to March in southern India. However, from circumstantial
evidence, it appears that, in Lakshadweep breeding takes place from June
onwards. Suheli Valiyakara and Parli, in the Bangaram atoll, where Grey
Herons nest, are uninhabited islands visited by islanders from October to
May. Young Grey Herons were brought to Kavaratti as pets from Suheli
Valiyakara in October, by people visiting the atoll after the monsoon. On
both the occasions the atoll was visited, the Black-capped Kingfisher
Halcyon pileata was observed. The marine life around Suheli is so rich that
a proposal has been made to declare this area as a Marine National Park
(Menon 1976).
Bangaram atoll is situated at 10°56’N 72°17’E, north-east of Agatti, and
is visible from the latter. There are two larger islands, Bangaram and
Tinnakara, and two smaller islands, Parli 1 and Parli 2 within the lagoon;
56
D. N. KURUP and V. J. ZACHARIAS
Forktail 10
all are uninhabited. Bangaram is the largest island in the atoll and is
characterised by a 1 km long linear brackish water pond at the centre of the
island, extending to the northern extremity. The pond is fringed by Coconut
Palms and Pandanus thicket. The northern and southern ends of the island
have thick vegetation and the beach at several places above high water mark
is carpeted by ground vegetation, consisting of Cyperus and Spinifex littorens.
The beach consists of a fine sediment of corals and a variety of shorebirds
frequent the intertidal area. The fringes of the pond at low tide provide a
varied habitat of mudflat and shallows for a variety of wading birds. There
are many exposed sandbanks at the fringes of the reef where hundreds of
terns, particularly S. bergii and 5. bengalensis congregate.
Table 2 gives estimates of the numbers of terns observed in the different
atolls visited. It therefore appears that, except at Pitti, where S. fuscata and
A. stolidus are the predominant species, in all the other atolls 5. bergii and 5.
bengalensis are the commoner species, occurring in approximately equal
proportions.
Such observations, as described above, point to the state of flux regarding
the status of populations of terns in the different atolls. Until about the
1830s enormous numbers of seabirds used to breed in Bitra (Betts 1939).
When Hume visited the island in 1876, Bitra was still uninhabited but
people used to visit the island for tending the coconuts. As recently as 1963,
Mathew and Ambedkar observed 5. anaethetus and 5. bergii breeding at
Baliapannium. It is probably the cumulative effect of population increase
and the consequent proliferation of plantations; camping on the uninhabited
islets by fishermen; and direct predation of eggs, that have contributed to
either the cessation of breeding activity in certain islets, or to the shifting of
entire breeding colonies from one locality to another. Anyhow, the single
greatest threat to the breeding colonies of seabirds of the Lakshadweep
archipelago appears to be large scale predation of tern eggs. Even though it
is a quarter of a century since Pitti was declared a bird sanctuary, the
islanders continue to plunder the eggs and the only respite for the birds
comes in the form of the monsoon, from May to September, when the reef
is inaccessible. It is to be noted, in this connection, that of the 20 S', fuscata
colonies in the western Indian Ocean, 10 have become extinct in the last
hundred years and 4 have become reduced in numbers (Feare 1984).
Among the factors that Feare suggests as having contributed to the decline
in numbers of seabirds are alteration of habitat, i.e. substitution of indigenous
vegetation with plantations, usually of coconuts; guano extraction;
introduction of exotic animals; and direct predation of eggs. Of these, the
first and last are relevant to Lakshadweep.
1994
Birds of Lakshadweep Islands, India
57
RESULTS
The species of birds observed in Lakshadweep are listed in the appendix,
together with a summary of observations reported by other authors - a total
of 82 species.
On Kavaratti, the arrival of the first northern migrants coincided with the
waning of the south-west monsoon in September; by November most of the
birds had arrived. The numbers and variety were maintained until about the
second week of April when, quite abruptly, the number of birds declined,
indicating their departure. A surge in numbers was observed once in
November and for a second time towards April. Remnant migrants were
encountered as late as the last week of May. June and July, the monsoon
months, were practically bereft of birds, although the Mongolian Plover
Charadrius mongolus was occasionally sighted. The Mongolian Plover was
found to be the most abundant species on Kavaratti, closely followed by the
Ruddy Turnstone. In almost all the other islands surveyed, the Ruddy
Turnstone vastly outnumbered any other shorebird species. Even on such
dry reef flats as Pitti and Baliapannium, large flocks of Ruddy Turnstones
were met with. On all the islands except Kavaratti, the Grey Heron appeared
to be the second most abundant species. This resident species, however, was
found in greater numbers on uninhabited atolls such as Suheli and Bangaram.
Much of the avian activity on Kavaratti was concentrated at the southern
extremity of the island where no permanent human habitation exists. The
birds fed on small crustaceans, copepods and other invertebrates on the
intertidal shelf.
The children of Lakshadweep have a penchant for snaring birds with a
crude noose spread on the beach. The captured birds are pinioned and then
they are kept in households as pets. Several species, including Common
Teal Anas crecca , Ruddy Shelduck Tadomaferruginea , Whimbrel Numenius
phaeopus, Grey Heron, Cattle Egret Bubulcus ibis, Sooty Tern including
young ones, Ruddy Turnstone, Common Sandpiper Tringa hypoleucos,
Terek Sandpiper T. cinerea, and Rock Pigeon Columba livia were found.
The Oriental White-eye Zosterops palpebrosus is a resident species on
Kavaratti and Kadmat where it was observed in large numbers. On Kavaratti,
despite the greater population pressure and corresponding denudation of
plant cover, these small birds thrive, probably because the House Crow
Corvus splendens, a potential predator, is absent from this island. On
Kadmat, the White-eyes thrived, presumably because the natural vegetation
is more abundant and there is less population pressure on this island;
feeding parties consisting of 30-40 White-eyes were often seen on the
coconut fronds and inflorescences. Hume (1876) described it as occurring
in all the islands. However, during the present study, the bird was not met
with on Kalpeni, Amini, Suheli or Bitra.
58
D. N. KURUP and V. J. ZACHARIAS
Forktail 10
The Asian Koel Eudynamys scolopacea, Brown Shrike Lanius cristatus,
Greater Coucal Centropus sinensis , Black Kite Milvus migrans, Common
Kestrel Falco tinnunculus and Indian Roller Coracias benghalensis were
among the land birds recorded once or on several occasions during the study
period. The House Crow was not observed on Kavaratti though it was
present on Kalpeni, Amini, Kadmat and Minicoy. Two species of terns, the
Sooty Tern and Brown Noddy were observed breeding in large numbers on
Pitti. The Great Crested Tern and Lesser Crested Tern were also common
in the archipelago. The uninhabited atolls, Suheli and Bangaram, appeared
to support a relatively richer avifauna than the inhabited ones. Altogether 49
species were observed by us, of which 1 7 are new additions to the Lakshadweep
avifauna.
DISCUSSION
The occurrence and seasonal variation in numbers of different birds on
Kavaratti suggest that birdlife is generally scanty on Lakshadweep. While
this is largely true in the case of most of the inhabited islands, the variety and
numbers of birds are greater in certain uninhabited islands such as Suheli
and Bangaram. Observations by Hume (1876) and Mathew and Ambedkar
(1964) also lend credence to this view. Large breeding colonies of pelagic
terns were observed in reefs and islets such as Pitti. Though a majority of the
birds are migrants arriving from their Palearctic breeding grounds in the
north, a small percentage of southern hemisphere birds may also arrive, as
evidenced by the records of petrels and shearwaters (Mathew and Ambedkar
1964, Betts 1939). It is also possible that a small number of tropical
breeding birds arrive by island hopping from the south or from elsewhere.
Phillips (1963) noted that some exchange of birdlife took place between
Addu Atoll in south Maldives and Chagos archipelago in the south.
Possibly, those that spread across the Maldivian atolls do spill to some
extent into Lakshadweep and vice versa. The species profile and the pattern
of occurrence of birds studied on the west coast of Malabar in Kerala
(Kurup 1991) was found to be remarkably similar to those in Lakshadweep.
HUMAN POPULATION AND ITS IMPACT ON THE
ECOLOGY OF THE ISLANDS
The population density of each island is high, averaging about 4,000 per
island (1981 census) . There are numerous wells and tanks littered throughout
the inhabited islands, and there are many open pits used for defecation. The
extreme porosity of the calcareous soil and the high water table contribute
to the easy infiltration of nitrogenous waste materials into the freshwater
1994
Birds of Lakshadweep Islands, India
59
sources. This, together with the burial of dead bodies in the highly porous
soil, and the offal left over after the production of ‘mas’ from the tuna catch,
badly contaminate the ground water. Undoubtedly, the quality of the
environment in these areas has been affected. There is substantial quarrying
for coral boulders and shingle for construction purposes; if this continues at
the current rate, it is likely to affect even the physical existence of the coral
atolls. There is denudation of green cover almost everywhere as construction
activities have resulted in the large scale clearing of natural vegetation in all
the inhabited islands. Except for patches of Pemphis acidula and Scaevola
sericea most of the original vegetation of Kavaratti has been lost. Even
uninhabited islands are being used for coconut cultivation. All these factors
have probably affected birdlife too. Except for uninhabited atolls such as
Suheli and Bangaram, and the reefs of Pitti, Baliapannium and Perumal Par,
most other areas do not harbour a profuse avifauna any longer.
We are grateful to Dr. A. J. Gaston of the Canadian Wildlife Service for his constructive comments
on an early draft. The late Prof. R. M. Naik of Saurashtra University and the late Prof. K. K.
Neelakantan read through the paper and suggested necessary changes; we owe our thanks to them.
We thank the Administration of the U nion T erritory of Lakshadweep for giving us an opportunity to
study the birds (1985-1986) and also for providing logistical assistance during our trip to Suheli and
Pitti in 1988.
REFERENCES
Anon. (1991) Pitti Island, Lakshadweep: an ornithological study . Madras: Madras Naturalists’ Society.
Alcock, A. (1902) A naturalist in Indian seas. London: John Murray.
Ali, S. and Ripley, S. D. (1987) Compact handbook of the birds of India and Pakistan. Second ed. New
Delhi: Oxford University Press.
Betts, F. N. (1939) The birds of the Laccadive Islands. J. Bombay Nat. Hist. Soc. 40: 382-387.
Bhaskaran, S. T. (1985) Birding in Lakshadweep. Newletter for Birdwatchers 25(11 & 12): 9-10.
Burton, R. W. (1940) A visit to the Laccadive Islands. J. Bombay. Nat. Hist. Soc. 41: 489-513.
Daniels, R. J. R. (1992) Island biogeography and the birds of the Lakshadweep Archipelago, Indian
Ocean. J. Bombay. Nat. Hist. Soc. 88: 320-328.
Ellis, R. H. (1924) A short account of the Laccadive Islands and Minicoy. P. R. Madras Government
Press.
Feare, C. J. (1979) Ecology of the Bird Island, Seychelles. Atoll Research Bull. 226: 1-29.
Feare, C. J. (1984) Seabird status and conservation in the tropical Indian Ocean. Pp. 457-471 in J.P.
Croxall, P.G.H. Evans and R.W. Schreiber, eds. Status and conservation of the world’s seabirds.
Cambridge, U.K.: International Council for Bird Preservation (Technical Publication No. 2).
Gadow, H. and Gardiner, S. (1903) Aves. Pp. 368-373 in The fauna and geography of the Maidive and
Laccadive archipelagos. Cambridge: Cambridge University Press.
Government of India (1985) Coral paradise. Publication of the Administration ofthe Union Territory
of Lakshadweep.
Hume, A. O. (1876) The Laccadives and the west coast. Stray Feathers 4: 413-482.
Kurup, D. N. (1991) Ecology of the birds of Malabar coast and Lakshadweep. Ph.D. Thesis
submitted to the University of Calicut.
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D. N. KURUP and V. J. ZACHARIAS
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Livingston, P. (1987) Detection of tuna shoals from observations of sea birds in the skipjack pole and line
fishing of Lakshadweep. CMFRI special publication 40 abstract 32, 30-31.
Mannadiar, N. S. (1977) Lakshadweep, Gazetteer of India. Coimbatore.
Mathew, D. N. and Ambedkar, V. C. (1964) A bird study trip to the Laccadive Islands. J. Bombay
Nat. Hist. Soc. 61: 185-190.
Menon, A. G. K. (1976) Marine park in Lakshadweep: a report submitted to the Department of
Science and Technology, Government of India.
Mohan, R. S. Lai (1989) Some observations on the marine mammals and marine birds. CMFRI Bull.
43: 195-199.
Phillips, W. W. A. (1963) The birds of the Maidive islands, Indian Ocean. J. Bombay. Nat. Hist. Soc.
60: 546-584.
Pocklington, R. (1967) Observations by personnel of R. V. Atlantis II on islands in the Indian Ocean.
Sea Swallow 19: 38-41.
Ramunni, M. (1962) An atlas of Laccadive, Minicoy and Ammidive Islands. Madras.
Sivadasan, M. and Joseph, K. T. (1981) A botanical trip to Lakshadweep. Bull. Bot. Surv. India 23:
65-68.
Subiah, K. S. (1978) Pied Crested Cuckoo in Lakshadweep. Hombill January-March 1978: 2-3.
Tuck, G. S. (1964) Land birds at sea. Sea Swallow 16: 40-59.
Deepakumar Narayana Kurup, Silent Valley National Park, Mannarkkad P.O., Palakkad District,
Kerala India.
Dr V. J. Zacharias, Research Officer, Project Tiger, Thekkady, Kerala 685 536, India.
1994
Birds of Lakshadweep Islands, India
61
APPENDIX
SYSTEMATIC LIST OF THE BIRDS OF LAKSHADWEEP
Ruddy Shelduck Tadoma ferruginea. One captive individual was noted on Kavaratti.
Common TealAhos crecca. Several captive specimens were found on Kavaratti. Noted by Ellis, and Betts found a dried
head on Amini and was told they were regular winter visitors in varying numbers.
Garganey Anas querquedula. One noted in captivity in December 1988. Daniels saw it in April 1988.
Ferruginous Pochard Aychya nyroca. Daniels saw it in April 1988.
Eurasian Hoopoe Upupa epops. Sightings claimed by several islanders.
Indian Roller Coracias benghalensis. Observed several times on Kavaratti, between December and April. Burton saw
several on Chetlat and one on Bitra in November.
Common KingfisherH/chc/o atthis. Mathew and Ambedkar saw one on Kavaratti. Mohan (1 989) noted it on Bangram,
Tinnakara-Parali, Bitra and Kiltan.
White-throated Kingfisher Halcyon smymensis. One was seen on Bitra on 25 March 1986.
Black-capped Kingfisher Halcyon pileata. Observed on Suheli Valiyakara on both visits in 1 986 and 1988, and once
on Kavaratti in 1988.
Pied Cuckoo Oxylophus jacobitius. Recorded by Subiah (1978).
Common Cuckoo Cuculus canorus. Seen once on Kavaratti in December 1985.
Grey-bellied Cuckoo Cacomantis passerinus. Recorded by Anon. (1991).
Asian Koel Eudynamys scolopacea. Observed several times on Kavaratti. Hume found it on every inhabited island that
he visited. Forbes recorded it in February. Mathew and Ambedkar saw it on Agatti and Mohan (1989) saw it on Kiltan.
Daniels listed it as a resident. Recorded by Anon. (1991).
Rose-ringed Parakeet Psitracula krameri. Daniels saw it in April 1988, but noted that these were probably recently
escaped birds. Recorded by Anon. (1991).
Little Swift Apus affinis. Listed by Anon. (1991).
Asian Palm-Swift Cypsiurus balasiensis. Found on several occasions on Kavaratti.
Owl Strigidae. A large owl was flushed from Pemphis thicket on Kalpani in January 1986.
Brown Wood Owl Sirix leptogrammica. Noted on Bitra by Hume, who noted that it had been introduced to check
rodents.
Rock Pigeon Columba livia. Feral birds were common on Kavaratti.
Oriental Turtle-Dove Sireptopelia oricntalis . Mathew and Ambedkar collected one on Chetlat. Mohan (1989) noted
it on Suheli and Kalpani in 1987.
Crake Porzana. One seen near the brackish water pond on Suheli Cheriyakara in December 1988. Listed by Anon.
(1991) as Little Crake P. parva but the identification was not confirmed.
White-breasted Waterhen Amauromis phoenicurus. One seen in Pandanus thicket near the brackish water pond on
Bangaram. Gadow and Gardiner took a young bird from a nest on Minicoy at the end of July, 1899. Ellis recorded
it as a resident and Daniels saw one on Minicoy in April 1988. Burton saw a ‘water rail, unidentified’ on Bitra. Seen
by Anon. (1991).
Snipe Gallinago. Seen on Kalpeni, Bangaram and Suheli Cheriyakara.
Bar-tailed Godwit Limosa lapponica. Six were seen on Kalpani.
Black-tailed Godwit Limosa limosa. Seen once on Kavaratti in April 1986.
W himbrel Numenius phaeopus. Found in small numbers on almost all the islands visited. A flock of 12 was seen on
Parli in April 1986. Mathew and Ambedkar saw one about 10 miles off Kavrathi. Recorded by Anon. (1991).
Eurasian Curlew Numenius arquata. Far less common than Whimbrel, but seen on Suheli and Bangaram in large
numbers. Hume collected it on Kadmat and Agatti, and Mathew and Ambedkar saw three on Bitra. Recorded by
Anon. (1991).
Common Redshank Tringa tolanus. Seen on Bangaram and one was found in captivity on Kavaratti.
Common Greenshank Tringa nebularia. Found throughout the winter, in small numbers, in all the atolls. Only
recorded previously by Hume who shot one on Kadmat. Recorded by Anon. (1991).
Green Sandpiper Tringa ochropus. Noted on Kavaratti and Bangaram.
Wood Sandpiper Tringa glareola. Singles noted on Kavaratti and Suheli Cheriyakara.
Terek Sandpiper Tringa cinerea. Several noted in captivity on Kavaratti. Recorded by Anon. (1991).
Common Sandpiper Tringa hypoleucos. The most numerous wader after Ruddy Turnstone. Usually seen singly or in
pairs, but 10 were noted roosting on a floating platform in the Bangaram lagoon. Gadow and Gardiner saw it on
Minicoy in August. Recorded by Anon. (1991).
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D. N. KURUP and V. J. ZAC H ARIAS
Forktail 10
Ruddy Turnstone A renaria ituerpres. The commonest wader: a flock of 500 was noted on Baliapannium atoll. Hume
also found it to be the commonest bird, and it is strange that it is not mentioned by Ellis nor by Betts. Recorded by
Anon. (1991).
Great Knot Calidris tenuirosiris. Only recorded by Hume, who saw two on Bitra.
Sanderling Calidris alba. Three were noted on Suheli Pitti. Hume collected two on Bitra. Recorded by Anon. (1991).
Little Stint Calidris minuta. Mathew and Ambedkar saw it on the coral reefs on Agatti, Chetlat and Bitra. Recorded
by Mohan (1989) on six different islands and by Anon. (1991). Burton saw ‘stints’ on Bitra.
Eurasian Thick-knee Burhinus oedicnernus. Observed once on 1 4 November 1 985 at the northern extremity of Kadmat.
Black-winged Stilt Himantopus himantopus. Daniels saw it once in April 1988.
Eurasian Avocet Recurvirostra avosetta. Burton saw some on Bitra.
Pacific Golden Plover Pluvialis fulva. More numerous on Kavaratti than the Grey Plover. Gadow and Gardiner
recorded it on Minicoy and Mathew and Ambedkar saw it on Chetlat and Bitra. Recorded by Anon. (1991).
Grey Plover Pluvialis squatarola. Apparently a winter visitor to all the islands, although Betts did not record it and
Mathew and Ambedkar only saw a single bird on Chetlat. Recorded by Anon. (1981).
Kentish Plover Charadrius alexandrinus. Seen only on Suheli Cheriyakara. Recorded by Hume, and Mathew and
Ambedkar saw it in flocks of 8 to 10 on Chetlat and Bitra.
Mongolian Plover Charadrius mongolus . One of the commonest waders, found in all the islands. Hume collected
three on Kadmat, but saw no others. Betts collected one out of a flock of six on Kiltan, the only ones he saw. Recorded
by Anon. (1991).
Greater Sand Plover Charadrius leschenaultii. Sparingly distributed; in greatest numbers on Suheli Valiyakara.
Hume collected it on Kadmat and Kiltan.
Crab Plover Dromas ardeola. A flock of 10 was seen on Suheli Pitti in December 1988. Hume noted a flock on
Perumalpar and Mathew and Ambedkar saw a pair on Bitra. Daniels saw it in April 1988. Recorded by Anon. (1991).
South Polar Skua Caiharacta maccormicki. Daniels saw it in April 1988. In addition Mathew and Ambedkar saw
unidentified skuas near Baliapannium atoll and between Calicut and Kavrathi.
Pomarine Jaeger Stercorarius pomarinus. Daniels saw it in April 1988, and Pocklington (1967) saw a bird, probably
of this species, on 5 April 1965.
Parasitic Jaeger Stercorarius parasiticus. Daniels saw it in April 1988.
Lesser Black-backed Gull Larus fuscus. One was noted in captivity on Kavaratti. Burton mentions ‘a number of sea
gulls’ on Bitra and Kadmat.
Gull-billed Tern Sterna nilotica. Seen by Anon. (1991).
Lesser Crested-Tern Sterna bengalensis. Found with Great Crested-Terns but in smaller numbers. May breed on
Pitti. Recorded by Anon. (1991).
Great Crested-Tern Sterna bergii. Found in large concentrations near Baliapannium (250), Perumal Par, (280),
Bangaram and Suheli atolls. Eggs were collected on Pitti in April 1986. Recorded by Anon. (1991).
Little Tern Sterna albifrons. Hume collected several on Baliapannium. Recorded by Anon. (1991).
White-cheeked Tern Sterna repressa. Hume collected two immatures on Baliapannium.
Bridled Tern Sterna anaethetus. Hume noted it on Baliapannium, and Mathew and Ambedkar ringed chicks there;
however, none was seen in April 1986.
Sooty Tern Sterna fuscata. Between 5,000 and 6,000 were seen on Pitti in December 1988. Young birds were
collected and taken to Kavaratti in October 1985. Recorded by Anon. (1991).
Brown Noddy Atious stolidus. Between 8,000 and 9,000 were found with many Sooty Terns on Pitti in December
1988. Recorded by Anon. (1991).
Lesser Noddy Anous tenuirosiris. Recorded on Minicoy.
Osprey Pandion haliaetus. Betts saw one on Kadmat and one on Kiltan.
Black-winged Kite Elanus caeruleus. Recorded by Hume, who collected it on Amini and Kadmat.
Black Kite Milvus migrans. A winter visitor to Kavaratti, observed between September and March.
White-bellied Fish-Eagle Haliaaetus leucogaster. Only noted by Hume who saw one soaring over Amini.
Western Marsh-Harrier Circus aeruginosus. One was seen flying low over the lagoon near Suheli Valiyakara. Listed
by Daniels.
Pallid Harrier Circus macrourus. Recorded by Ellis; Burton, who noted it on Chetlat; and Betts, who saw two on Kiltan.
Montagu’s Harrier Circus pygargus. Recorded By Ellis and Burton, who saw it on Bitra.
Shikra Accipiter badius. Seen once on Kavaratti in December 1988.
Common Kestrel Falco tinnunculus . One noted at the southern end of Kavaratti. Hume found it on all of the islands
he visited. Betts recorded it on Amini and Kadmat. Recorded by Anon. (1991).
Peregrine Falcon Falco peregrinus. Hume described it as a regular migrant.
Red-billed Tropicbird Phaethon aethereus. Recorded by Hume: 30 miles from Baliapannium; and Betts: two during
the passage from the mainland, but at least 50 miles from the nearest shore. Daniels saw it in April 1988.
Masked Booby Sula dactylatra. Daniels listed it as a resident. Feare listed it as a questionable breeding species.
1994
Birds of Lakshadweep Islands, India
63
Red-footed Booby Sula sula. Hume saw a large flock of what he believed to be this species near Perumal Par. Daniels
listed it as a resident. Feare listed it as a questionable breeding species.
Brown Booby Sula leucogasler. Hume saw one on Baliapannium, and collected one on Perumal Par. Daniels listed
it as a resident. Feare listed it as a questionable breeding species.
Great Cormorant Phalacrocorax carbo. Listed by Anon. (1991).
Little Egret Egretta garzetta. Noted uncommonly on Kavaratti, Bangaram and Suheli Cheriyakara. Gadow and
Gardiner saw one on Minicoy in July 1 899. Daniels saw it in April 1 988 and listed it as a possible resident. Recorded
by Anon. (1991).
Western Reef-Egret Egretta gularis. One was seen by Hume on Bitra, and it was possibly seen on Kavaratti by
Mathew and Ambedkar. Daniels listed it as a possible resident. Recorded by Anon. (1991).
Grey Heron Ardea cinerea. Found in small numbers in almost all the atolls, and found breeding on Suheli Valiyakara
and Parli islet. Hume suspected that it bred on Agatti (not Bangaram as reported by Betts) because he noted stick
nests in two or three trees. Gadow and Gardiner, and Ellis, mentioned a breeding colony on Viringilli, a small islet
in the Minicoy lagoon.
Purple Heron Ardea purpurea. Seen by Anon. (1991).
Cattle Egret Bubulcus ibis. Found between November and April on Kavaratti; a flock was noted on Kadmat . Daniels
saw it in April 1988 and listed it as a possible resident. Recorded by Anon. (1991).
Indian Pond-Heron Ardeola grayii . Observed on Kavaratti, Suheli Cheriyakara and Bangaram. Hume saw it on Amini
and on Kadmat, Betts saw one on Amini, and Mathew and Ambedkar saw one about 1 5 miles off Bitra. Daniels listed
it as a possible resident. Recorded by Anon. (1991).
Striated Heron Butorides striacus. Hume collected one on Kadmat and Betts saw one on Amini. Daniels saw one in
breeding plumage in April 1988. Recorded by Anon. (1991).
Yellow Bittern Ixobrychus sinensis. Seen by Anon. (1991).
Stork Ciconiidae. Burton saw a ‘large black and white stork’ on Bitra.
Great Frigatebird Fregata minor. Listed by Anon. (1991).
W edge-tailed Shearwater Puffinus pacificus. Betts mentioned several solitary shearwaters with dark underparts seen
during the passage from the Malabar coast. Daniels saw it in April 1988.
Audubon’s Shearwater Puffinus Iherminieri. Ellis considered itto be a resident species. Feare listed it as a questionable
breeding species.
Jouanin’s Petrel Bulweria fallax. Daniels saw it in April 1988, and Pocklington (1967) saw ‘dark gadfly petrels’,
probably of this species, on 5 September 1963.
Wilson’s Storm-Petrel Oceanites oceanicus. Only found once, about 28 km off Cochin, but local fishermen
considered that it was not uncommon. Previously recorded by Mathew and Ambedkar between Calicut and Kavrathi,
and by Mohan (1989) off various islands in early 1987.
Swinhoe’s Storm-Petrel Oceanodroma monorhis. Mathew and Ambedkar noted one caught on a ship between Chetlat
and Bitra on 20 October 1963. Mohan ( 1 989) noted very small numbers off Agatti, Bangram, Tinnakara-Parali, Bitra
and Kadmat during a visit from January to April 1987. Pocklington (1967) saw ‘more than 35 dark storm-petrels’,
probably this species, at 10°53’N 72°45’E on 15 March 1965.
Indian Pitta Pitta brachyura. Seen by Anon. (1991).
Brown Shrike Lanius cristatus. Observed on several occasions on Kavaratti between November and April, and seen
once on Kadmat. Betts saw one on Kiltan. Seen by Anon. (1991).
House Crow Corvus splendens. Betts described it as occurring only on Kalpeni, Amini and Androth. It now occurs
on Kadmat and has reportedly been introduced on Minicoy. Daniels listed it as an introduced resident.
Common Myna Acridotheres tristis. Ali and Ripley (1983) mention that it was introduced to Lakshadweep but give no
further details. It has not been recorded by any of the surveys.
Sand Martin Riparia riparia. Recorded by Anon. (1991).
Barn Swallow Hirundo rustica. Gadow and Gardiner saw several on Minicoy between 1 and 4 September. Mathew
and Ambedkar saw a few birds off Kavaratti. Mohan (1989) noted it on Bitra, Kiltan and Amini in 1987. Daniels saw
it in April 1988. Seen by Anon. (1991).
Red-rumped Swallow Hirundo daurica. A large flock was seen on Suheli Cheriyakara.
Northern House-Martin Delichon urbica. Recorded by Ellis; also by Mathew and Ambedkar: one on a ship between
Calicut and Kavaratti, and a flock of 1 0 on Chetlat.
Oriental White-eye Zosterops palpebrosus. The only resident species on the majority of the islands. It was numerous
on Kadmat and Kavaratti, and was found breeding on the latter. Mohan (1989) noted it on Agatti, Bangram,
Tinnakara-Parali and Bitra, and it has also been reported from Androth, Chetlat and Suheli Valiyakara.
Blyth’s Reed-Warbler Acrocephalus dumetorum. Recorded by Anon. (1991).
White Wagtail Motacilla alba. Recorded by Anon. (1991).
Yellow Wagtail Motacilla /lava. Two were seen on Suheli Cheriyakara in December 1988. Mathew and Ambedkar
saw a ‘flock of some six birds’, apparently of the race thunbergi, on Bitra. Daniels saw it in April 1 988. Seen by Anon.
(1991).
64
D. N. KURUP and V. J. ZACHARIAS
Forktail 10
Grey Wagtail Motacilla cinerea. Recorded off Lakshadweep at 12°32’N 74°10’E on 3 October 1962 (Tuck 1964).
Richard’s Pipit Atithus richardi. Recorded by Anon. (1991).
Tree Pipit Atithus trivialis. Recorded by Anon. (1991).
Pipit Ambus. Mathew and Ambedkar saw one on the coral reef on Bitra.
1994
FORKTAIL 10 (1994) 65 - 104
65
Recent bird records from
Arunachal Pradesh
PRATAP SINGH
Very little information exists on the avifauna of Arunachal Pradesh. A compilation of bird records
gathered from 1 988 to 1 994 is presented. A complete list of the 5 1 9 species recorded is given, together
with information on localities, habitats and altitudinal ranges. A number of important records are
given in more detail, including several globally threatened species and some new records for
Arunachal Pradesh. A list of 138 extra species recorded in Arunachal Pradesh by other authors is
given in an appendix.
The avifauna of the eastern Himalaya, particularly that of Arunachal
Pradesh, has not been exhaustively surveyed. There are very few published
accounts relating to birds in Arunachal Pradesh: Ali and Ripley (1948),
Bailey (1916), Baker (1913a and b, 1914a and b), Betts (1954, 1956),
Chatterjee and Chandiramani (1986), Choudhury (1990, 1992, 1993),
Ghosh (1987), Godwin-Austen (1875, 1876a and b, 1877), Katti (1992),
Katti et al. (1992), Kaul and Ahmed (1992), Ludlow and Kinnear (1937,
1 944), Pandya ( 1 990), Parsons ( 1 935, 1 939a and b), Ripley ( 1 948), Ripley
(1980), Ripley et al. (1991), Saha (1981, 1985), Singh (1993), Stevens
(1915), Stonor (1952) and Whistler (1941). Out of 71 globally threatened
species of birds recorded in India (N. J. Collar, M. J. Crosby and A. J.
Stattersfield, 1 994, Birds to watch 2, the world list of threatened birds), 26 have
been recorded in Arunachal Pradesh (Appendices 1 and 2) and 13 of these
were recorded during this survey. These species are indicated by an asterisk
(*) in this paper.
*Swamp Francolin Francolinus gularis Seen at D’Ering WLS on 29 January
1994. The first record for Arunachal Pradesh.
* Chestnut-breasted Partridge Arborophila mandellii A dead bird was
seen at Malinye ( 1 ,850 m) on 10 January 1 994. A little-known species with
very few records from anywhere in its range.
*Ferruginous Pochard Aythya nyroca Seen at D’Ering WLS (120 m).
Common Goldeneye Bucephala clangula Seen at D’Ering WLS on 13 and
1 5 March 1 993, and 28-29 January 1 994. Previously recorded in Arunachal
Pradesh only by Choudhury (1992) who saw one on 17 March 1991.
Yellow-rumped Honeyguide Indicator xanthonotus One was noted on a tree
branch near a honeycomb at Limeking (1,450 m) on 14 November 1992,
and another was seen near Pange (1,700 m) on 18 March 1994. The first
records for Arunachal Pradesh.
66
PRATAP SINGH
Forktail 10
Eurasian Wryneck Jynx torquilla Singles were seen at Kirsinghsa on 2
March 1993, at Naharlagun on 25 April 1993, on the Hayliang-Wallong
road on 5, 9 and 1 1 September 1994, and near Ditchu on 13 September
1994. The first records for Arunachal Pradesh.
Coppersmith Barbet Megalaima haemacephala Seen at Foothills (150 m)
on 22 April 1991, and at Naharlagun on 23 October 1993 and 22 January
1994. The first records for Arunachal Pradesh.
* Rufous-necked Hornbill Aceros nipalensis Seen at Keegut, Deban,
Khellong, Glao Lake, Pange, Tipi, Sessa, Hayliang road and Mehao lake
track.
*W ard’sTrogon Harpactes wardi Recorded at Chakoo, Alinye and Helmet
Top between 2,000 and 3,000 m.
Black-capped Kingfisher Halcyon pileata A single was seen near the
Foothills Range headquarters ( 1 50 m) on 2 1 April 1991, and a skin from this
species, purportedly locally killed, was noted at Hotspring (3,300 m) in
September 1991. The first records for Arunachal Pradesh.
Blue-tailed Bee-eater Merops philippinus Seen at Chessa on 8 September
1991 and at Seijusa on 9 October 1994. The first records for Arunachal
Pradesh.
Asian Emerald Cuckoo Chrysococcyx maculatus A female was seen near
Talley valley at 2,200 m, a very high altitude for the species. Previously listed
by Ripley (1982) for Arunachal Pradesh but this is the first specific
published record.
Violet Cuckoo Chrysococcyx xanthorhynchus A pair was seen near Namora
(150 m) on 24 April 1992, and a male was seen near Jang (2,400 m) on 6
May 1993. The first records for Arunachal Pradesh.
Derbyan Parakeet Psittacula derbiana Many were seen at Hotspring (3,399
m) from 25 to 29 September 1991. The birds made frequent visits to nest-
holes in a tall dead tree. Previously only recorded further west in Siang and
Subansiri districts (Stonor 1952).
Silver-backed Needletail Hirundapus cochinchinensis Seen at Talley
Valley (2,400 m) on 22-24 March 1994, at Yachuli (1,200 m) on 10
November 1993, and at Seijusa (150 m) on 11 April 1993. The first records
for Arunachal Pradesh.
Eurasian Eagle-Owl Bubo bubo One was caught near Taksing (2,300 m)
on 2 December 1992. The first record for Arunachal Pradesh.
Great Eared-Nightj ar Eurostopodus macrotis One was heard at Mehao lake
(1,650 m) on 13 November 1994. The first record for Arunachal Pradesh.
Eurasian Collared-Dove Streptopelia decaocto Seen at D’Ering WLS on 12
November 1991 and 14-15 March 1993. The first records for Arunachal
Pradesh.
1994
Recent bird records from Arunachal Pradesh
67
*Bengal Florican Eupodotis bengalensis Seen at D’Ering WLS on 2
November 1991 and 14-15 March 1993. Listed by Ripley (1982) for
Arunachal Pradesh but no definite records.
Brown Crake Am auromis akool Seen at Chessa on 1 1 April 1992. The first
record for Arunachal Pradesh.
V^hite-breasted W aterhen Amauromis phoenicurus Seen at Namsai on 30
January 1992. The first record for Arunachal Pradesh.
Black-tailed Crake Amauromis bicolor A single was seen in a swampy area
at Pange on 24 June 1991. Previously recorded at Lhalung by Ludlow and
Kinnear (1944) (Inskipp and Round 1989).
Black-tailed Godwit Limosa limosa Seen at D’Ering WLS, Khari and
Namora. The first records for Arunachal Pradesh.
Great Thick-knee Burhinus recurvirostris Seen at D’Ering (120 m) on 28
January 1994. Recorded in Arunachal Pradesh previously only by Choudhury
(1992).
Great Black-headed Gull Larus ichthyaetus Seen at Tezu on 4 March
1988 and also seen at D’Ering, Namora and Miao. The first records for
Arunachal Pradesh.
Brown-headed Gull Larus brunnicephalus Seen at D’Ering WLS on 13
December 1991; also at Miao (100 m) and at Seijusa (120 m). The first
records for Arunachal Pradesh.
*Black-bellied Tern Sterna acuticauda Seen at D’Ering WLS and at Tezu.
Oriental Honey-buzzard Pemis ptilorhyncus Seen at Khari on 19 August
1990 and at Seijusa on 6 February 1991. The first records for Arunachal
Pradesh.
White-tailed Eagle Haliaeetus albicilla Seen at D’Ering WLS on 1 3 March
1993 and at Deban on 12 February 1994. The first records for Arunachal
Pradesh.
Eurasian Griffon Gyps fulvus Seen at Mayodia (2,500 m) on 29 December
1993 and 1 January 1994. The first record for Arunachal Pradesh.
Short-toed Snake-Eagle Circaetus gallicus Singles were seen at Anchal
Ghat in D’Ering WLS on 3 November 1991 and 1 5 March 1993. The only
records for Arunachal Pradesh.
*Lesser Kestrel Falco naumanni Seen at Naharlagun on 27 October 1992.
The first record for Arunachal Pradesh.
Amur Falcon Falco amurensis Large numbers were seen at Naharlagun
during the last week of October 1992. The first record for Arunachal
Pradesh.
Merlin Falco columbarius One was seen on 15 March 1993 in D’Ering
WLS. It settled on a driftwood stack in the riverbed of Siang. The first
record for Arunachal Pradesh and north-east India.
68
PRATAP SINGH
Forktail 10
Eurasian Hobby Falco subbuteo Three were seen near Wallong on 6 October
1991. The first record for Arunachal Pradesh.
Black-crowned Night-Heron Nycticorax nycticorax Seen at Tezu on 16
April 1988. The first record for Arunachal Pradesh.
Black-headed Ibis Threskiomis melanocephalus Seen over Khari on 19
August 1990. The first record for Arunachal Pradesh.
Black Stork Ciconia nigra Seen at D’Ering WLS and over Khari. The first
records for Arunachal Pradesh.
Woolly-necked Stork Ciconia episcopus Seen over Namsai. The first
record for Arunachal Pradesh.
Black-necked Stork Ephippiorhynchus asiaticus Seen at D’Ering on 13-14
December 1991 and on 29 January 1994. Not recorded in Arunachal
Pradesh by Rahmani ( 1 989) and the species is now very reduced in numbers
in Asia, especially in the Indian subcontinent.
*Lesser Adjutant Leptoptilos javanicus Recorded at D’Ering WLS.
Blue-winged Leafbird Chloropsis cochinchinensis Seen on the Deban-
Ranijheel trek on 9-12 February 1994 with P. Alstrom and other Swedish
birdwatchers. The first record for Arunachal Pradesh.
Brown Shrike Lanius cristatus Listed for Arunachal Pradesh only by Ali and
Ripley (1987).
Rufous Treepie Dendrocitta vagabunda Listed for Arunachal Pradesh only
by Ripley (1982).
Chestnut Thrush Turdns rubrocanus Two were seen atMayodia (2,700 m)
on 5 January 1991, and one was seen near Wakro (300 m) on 27 January
1992. Previously recorded in Arunachal Pradesh by Katti et al. (1991).
Tickell’s Blue-Flycatcher Cyomis tickelliae Seen at Naharlagun (200 m)
on 30 April 1994. The first record for Arunachal Pradesh.
Purple Cochoa Cochoa purpurea A juvenile was seen near Pange (1,850 m)
on 13 June 1994. The first record for Arunachal Pradesh.
Great Myna Acridotheres grandis Seen occasionally at Naharlagun. Previously
recorded in Arunachal Pradesh only by Ripley et al. (1991).
Chestnut-vented Nuthatch Sitta nagaensis Seen at Kibitho ( 1 ,400 m) on
6 September 1994, at Milinja (2,400 m) on 14 September 1994, and at
Hotspring (3,200 m) on 1 6 September 1994. The first records for Arunachal
Pradesh.
*Beautiful Nuthatch Sitta formosa Seen at Sesni (1,300 m) on 21 April
1992, on the Etalin-Malinye track on 6 January 1994, at Hornbill on 1 1
February 1994, and at Sessa on 26 June 1994.
Eurasian Tree-creeper Certhia familaris Seen at Talley Valley, Hotspring
and Mago. Ripley (1982) stated that, following Ludlow and Kinnear
(1944), it occurred in Towang and the Pachakshiri region; however, the
1994
Recent bird records from Arunachal Pradesh
69
latter is an error because Ludlow’s specimens were from Tibet. The
Hotspring record is thus a considerable eastward extension of the range of
the species in the Himalaya.
Bar-tailed Treecreeper Certhia himalayana Seen at Kibitho (1,300 m) on
12 September 1994. The first record for Arunachal Pradesh.
Fire-capped Tit Cephalopyrus flammiceps One was seen in degraded
broadleaved/scrub forest near Bomdilla on 26 August 1 990. The first record
for Arunachal Pradesh, although subsequently seen by Katti (1992).
Rufous- vented Tit Pams mbidiventris Seen in the Thingbu-Mago area in
September 1990 and, commonly, in the same area during the first week of
May, 1993. Previously recorded in Arunachal Pradesh by Ludlow and
Kinnear (1937).
Sand Martin Riparia riparia Seen in the upper Dikroi on 9 February 1991.
The first record for Arunachal Pradesh.
Crested Finchbill Spizixos canifrons Two were seen near Glao Lake on 27
January 1992. The first record for Arunachal Pradesh.
Zitting Cisticola Cisticola juncidis Seen at D’Ering on 3 November 1991.
The first record for Arunachal Pradesh.
Golden-spectacled Warbler Seicercus burkii Birds of the subspecies
tephrocephalus were seen at Karoti on 22 September 1991 (two) and near
Ditchu on 23 September 1991 (at least three).
Rufous-rumped Grassbird Graminicola bengalensis Seen at D’Ering on 1 3
March 1993. The first record for Arunachal Pradesh.
Elliot’s Laughingthrush Gamdax elliotii A group of more than 20 was
seen near Hotspring (3,200 m) on 15 September 1994. The first record for
the Indian subcontinent.
Chestnut-crowned Laughingthrush Gamdax erythrocephalus Seen at
Wakro in January 1992 at the very low altitude of 300 m.
* Marsh Babbler Pellomeum palustre Two were seen at Tipi (400 m) on 26
June 1994. Previously listed for Arunachal Pradesh only by Ripley (1982).
* Rufous-throated Wren-Babbler Spelaeomis caudatus Seen in the
undergrowth of evergreen subtropical/temperate forest at Pange and Talley
valley (1,900-2,400 m), from 21 to 24 June 1991 and very commonly in
February and June 1994. Ripley (1982) mentions a specimen collected at
Khalaktang, Kameng district on 2 February 1978, but this is the only other
record for Arunachal Pradesh.
Bar- winged Wren-Babbler Spelaeomis troglodytoides A group of at least six
was seen near Chakoo (3,000 m) on 27 April 1991 (Singh 1992). Previously
recorded in Arunachal Pradesh by Ludlow and Kinnear (1944) from Nyug
La, and by Ripley et al. (1991) from Noa-Dihing.
Spotted Wren-Babbler Spelaeomis formosus Seen at Rani Jheel (500 m) on
70
PRATAP SINGH
Forktail 10
11 February 1994 and confirmed by P. Alstrom. The first record for
Arunachal Pradesh.
Long-tailed Wren-Babbler Spelaeomis chocolatinus Seen at Hotspring
(3,100 m) on 16 September 1994. Previously recorded from Arunachal
Pradesh only by Ripley et al. (1991).
Wedge-billed Wren-Babbler Sphenocichla humei The species was seen
many times in flocks of up to eight or more, in primary subtropical forest in
the Orak-Glenshang area (1,100-1,300 m) from 18 to 20 November 1992,
and also seen near Mehao lake on 1 4 November 1 994. Previously recorded
in Arunachal Pradesh by Baker (1922) from the Abor Hills, Ripley et al.
(1991) and by Katti et al. (1992).
*Snowy-throated Babbler Stachyris oglei Recorded on the Deban-Hombill
track at 450 m.
Chestnut-capped Babbler Timalia pileata Seen at Dimbey in March 1988
and at D’Ering WLS on 14 December 1991. Previously recorded in
Arunachal Pradesh by Abdulali (1983), and subsequently by Pandya
(1990).
Striated Babbler Turdoides earlei Seen at D’Ering on 2-3 November 1991
and near Tezu on 18 September 1994. The first records for Arunachal
Pradesh.
Brown Parrotbill Paradoxomis unicolor Seen on the Mago trek and at
Mayodia, and at Talley valley on 17 June 1994. Previously recorded at
Towang (Ali and Ripley 1987).
Spot-breasted Parrotbill Paradoxomis guttaticollis A group of at least five
birds was seen near Wallong (2,000 m) on 7 October 1991. The first record
for Arunachal Pradesh.
Greater Rufous-headed Parrotbill Paradoxomis mficeps Seen at Khellong,
Anini and Deban between 200 and 1 ,500 m. Treated as globally threatened
by Collar and Andrew (1988).
Indian Short-toed Lark Calandrella raytal Seen at D’Ering on 15 March
1993. The first record for Arunachal Pradesh.
Ruby-cheeked SuNBiRDHnt/zreptes singalensis Singles were seen at Deomali
on 24 January 1992 and at Chessa on 1 1 April 1992. Listed by Ripley (1982)
for Arunachal Pradesh.
White-browed Wagtail Motacilla maderaspatensis Seen at Tezu on 17
September 1991. The first record for Arunachal Pradesh.
Tawny Pipit Anthus campestris Many were seen near Tezu Forest Resthouse
on 1 1 October 1991, one was seen near Deomali on 24 January 1992 and
one at Hapoli on 27 March 1994. The first records for Arunachal Pradesh.
Baya Weaver Ploceus philippinus Seen at Naharlagun (200 m) on 29 May
1994. The first positive record for Arunachal Pradesh.
1994
Recent bird records from Arunachal Pradesh
71
Yellow-breasted Greenfinch Carduelis spinoides Listed by Ripley ( 1 982)
for Arunachal Pradesh.
Black-headed Greenfinch Carduelis ambigua Ripley (1982) listed it for
southeastern Tibet and adjacent parts of Arunachal Pradesh’, presumably
based on Ludlow s records. However, all Ludlow’s specimens were from
Tibet, making this the first record for Arunachal Pradesh and India.
Common Rosefinch Carpodacus erythrinus Seen frequently at Hotspring
from 27 to 29 September 1991. Previously recorded in Arunachal Pradesh
by Ali and Ripley (1948).
Spot-winged Rosefinch Carpodacus rodopeplus Seen at Mayodia (2,500 m)
on 31 December 1993. The first record for Arunachal Pradesh.
Godlewski’s Bunting Emberiza godlewskii Listed by Ripley (1982) for
Arunachal Pradesh, presumably based on Ludlow and Kinnear ( 1 944), but
all Ludlow’s specimens were from Tibet, as already pointed out by Ticehurst
(1941).
Yellow-breasted Bunting Emberiza aureola Seen on the Chakoo road on
25 April 1991. The first record for Arunachal Pradesh.
Jayant K. Kulkarni provided me constant guidance and sent me photocopies of bird literature
available in the library of the Bombay Natural History Society.
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1 . Abdulali, H. ( 1 983) A catalogue of the birds in the collection of Bombay Natural History Society
- 25 Muscicapidae (Timaliinae) (part). 7. Bombay Nat. Hist. Soc. 79: 336-360.
2. Ali, S. and Ripley, S. D. (1948) The birds of the Mishmi Hills. J. Bombay Nat. Hist. Soc. 48: 1-
37.
3. Ali, S. and Ripley, S. D. (1987) Compact handbook of the birds of India and Pakistan. New Delhi:
Oxford University Press.
4. Bailey, F. M. (1916) Notes from southern Tibet. J. Bombay Nat. Hist. Soc. 24: 72-78.
5. Baker, E. C. S. (1913a) Zoological results of the Abor Expedition (1911-1912). Birds. Rec.
Indian Mus. 8: 259-288.
6. Baker, E. C. S. (1913b) On a small collection of birds from the Mishmi Hills, N. E. frontier of
India. Rec. Indian Mus. 9: 251-254.
7. Baker, E. C. S. (191 4a) (Remarks on Crossoptilon harmani and Pomatorhinus erythrogenys.) Bull.
Brit. Om. Club 33: 121-124.
8. Baker, E. C. S. (1914b) (Description of new birds from the north-east frontier of India.) Bull.
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10. Betts, F. N. (1954) Occurrence of the Black-necked Crane ( Grus nigricollis ) in Indian limits. J.
Bombay Nat. Hist. Soc. 52: 605-606.
1 1. Betts, F. N. (1956) Notes on birds of the Subansiri area. J. Bombay Nat. Hist. Soc. 53: 397-414.
12. Blanford, W. T. and Oates, E.W. (1889-1898) Fauna of British India, birds. London: Taylor and
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13. Chatterjee, A. K. and Chandiramani, S. S. (1986) An introduction to Namdapha Tiger Reserve,
Arunachal Pradesh, India. Tigerpaper 13(3): 22-27.
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14. Choudhury, A. (1990) Bird observations from Namdapha National Park and adjacent areas.
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15. Choudhury, A. (1992) Some birds in D’Ering Sanctuary. Arunachal Forest News 10: 39-42.
16. Choudhury, A. (1993) Winter bird-count in Namdapha National Park. Unpublished.
17. Ghosh, A. K. (1987) Qualitative analysis of faunal resources of proposed Namdapha Biosphere
Reserve, Arunachal Pradesh. Calcutta: Zoological Survey of India.
18. Godwin-Austen, H. H. (1875) Description of a supposed new Actinura from the Dafla Hills.
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19. Godwin-Austen, H. H. (1876a) Description of a supposed new Suthora from the Dafla Hills and
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20. Godwin-Austen, H. H. (1876b) List of the birds collected on the expedition into the Dafla Hills,
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64-85.
21. Godwin-Austen, H. H. (1877) Description of three new species of birds of the genera Pellomeum,
Actinura and Pomatorhinus lately collected in the neighbourhood of Saddya, Assam, by Mr.
M. J. Ogle of the Topographical Survey. J. Asiatic Soc. Bengal 46(2): 41-45.
22. Hume, A. O. (1880) The game birds of India. Addenda et corrigenda. Stray Feathers 8: 489-494.
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24. Katti, M. (1992) Biodiversity and the exploitation of wild fruits in the tropical forests of
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25. Katti, M., Singh, P., Manjrekar, N., Mukherjee, S. and Sharma, D. (1992) An ornithological
survey in eastern Arunachal Pradesh, India. Forktail 7: 75-89.
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27. Ludlow, F. and Kinnear, N. B. (1937) The birds of Bhutan and adjacent territories of Sikkim
and Tibet. Ibis (14)1: 1-46, 249-293, 467-504.
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29. Pandya, N. P. (1990) Report on an initial survey of Pygmy Hog ( Sus salvanius ) and Hispid Hare
( Caprolagus hispidus ) and their habitat in Arunachal Pradesh. Unpublished.
30. Parsons, R. E. (1935) A second record of the occurrence of the Long-tailed Duck ( Clangula
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31 . Parsons, R. E. (1939a) Migration routes of geese. J. Bombay Nat. Hist. Soc. 40: 764-765.
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Bombay Nat. Hist. Soc. 41: 422-426.
33. Rahmani, A. R. (1989) Status of the Black-necked Stork Ephippiorhynchus asialicus in the Indian
subcontinent. Forktail 5: 99-110.
34. Ripley, S. D. (1948) New birds from Mishmi Hills. Proc. Biol. Soc. Washington 61: 99-107.
3 5 . Ripley, S . D . ( 1 980) A new species, and a new subspecies of bird from Tirap district, Arunachal
Pradesh, and comments on the subspecies of Stachyris nigriceps Blyth. J. Bombay Nat. Hist.
Soc. 77: 1-5.
36. Ripley, S. D. (1982) Synopsis of the birds of India and Pakistan.
37. Ripley, S. D., Saha, S. S. and Beehler, B. M. (1991) Notes on birds from the Upper Noa Dihing,
Arunachal Pradesh, northeastern India. Bull. Brit. Om. Club 111: 19-28.
38. Saha, S. S. (1981) Blacknecked Crane in Bhutan and Arunachal Pradesh - a survey report for
January-February 1978. J. Bombay Nat. Hist. Soc. 77: 326-328.
39. Saha, S. S. (1985) Aves. Records Zool. Surv. India 82: 303-318.
40. Singh, P. (1991a) A preliminary faunal survey in Thingbu Circle ofTowang District, Arunachal
Pradesh. Arunachal Forest News 9(1): 13-22.
41. Singh, P. (1991b) Avian and mammalian evidences in Pakhui Wildlife Sanctuary in East
Kameng District, Arunachal Pradesh. Arunachal Forest News 9(2): 1-10.
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Recent bird records from Arunachal Pradesh
73
42. Singh, P. (1991c) Sighting of Tibetan Blood Pheasant in Tawang District of Arunachal Pradesh.
W.P.A. News 32: 11-12.
43. Singh, P. (1993) Spotted Long-tailed Wren-Babbler Spelaeonris troglodytoides (Verreaux) in
Arunachal Pradesh. J. Bombay Nat. Hist. Soc. 89: 376.
44. Singh, P. (1993) Breeding record of Ferruginous Flycatcher Muscicapa ferruginea (Hodgson).
J. Bombay Nat. Hist. Soc. 90: 97-98.
45. Stevens, H. (1915) Notes on the birds of upper Assam. J. Bombay Nat. Hist. Soc. 23: 234-268,
547-570, 721-736.
46. Stonor, C. R. (1952) Distribution of Lord Derby’s Parakeet. Ibis 94: 162.
47. Ticehurst, C. B. (1941) Systematic notes on Indian birds. IX. 26. On some forms for the
inclusion ofwhich in the avifauna of British India further proof is needed (contd.). Ibis (14)5:
177-182.
48. Whistler, H. (1941) East Himalayan laughing thrushes. Ibis (14)5: 172-173.
Pratap Singh, DCF (Wildlife), Forest Department, PCCF Office, ltanagar 791111, Arunachal Pradesh,
India.
74
PRATAP SINGH
Forktail 10
APPENDIX 1
BIRDS RECORDED IN ARUNACHAL PRADESH, 1988-1994
Altitude Localities Habitat Abundance
Swamp Francoun Francolinus gularis
Hill Partridge Arborophila lorqueola
White-cheeked Partridge Arborophila atrogularis
Chestnut-breasted Partridge Arborophila mandellii
Blood Pheasant Ithaginis cruentus
Satyr Tragopan Tragopan sacyra
Temminck’s Tragopan Tragopan temminckii
Himalayan Monal Lophophorus impejanus
Red Junglefowl Gallus gallus
Kalij Pheasant Lophura leucomelanos
Grey Peacock-Pheasant Polyplectron bicalcaratum
Ruddy Shelduck Tadoma ferruginea
Gadwall Anas strepera
Eurasian Wigeon Anas penelope
Spot-billed Duck Anas poecilorhyncha
Northern Shoveler Anas clypeata
Northern Pintail Anas acuta
Garganey Anas querquedula
Common Teal Anas crecca
Ferruginous Pochard Aythya nyroca
Tufted Duck Aythya fuligula
Common Goldeneye Bucephala clangula
Common Merganser Mergus merganser
Buttonquail Tumix
Yellow-rumped Honeyguide Indicator xanthonotus
Eurasian Wryneck Jynx torquilla
Speckled Piculet Picumnus innominatus
1994
Recent bird records from Arunachal Pradesh
75
White-browed Piculet Sasia ochracea
Grey-capped Woodpecker Dendrocopos canicapillus
Fulvous-breasted Woodpecker Dendrocopos macei
Rufous-bellied Woodpecker Dendrocopos hyperythrus
Crimson-breasted Woodpecker Dendrocopos cathpharius
Darjeeling Woodpecker Dendrocopos darjellensis
Rufous Woodpecker Celeus brachyurus
Lesser Yellownape Picus chlorolophus
Greater Yellownape Picus Jlavinucha
Grey-headed Woodpecker Picus canus
Greater Flameback Chrysocolaptes lucidus
Pale-headed Woodpecker Gecinulus grantia
Bay Woodpecker Blythipicus pyrrhotis
Great Slaty Woodpecker Mulleripicus pulverulentus
Great Barbet Megalaima virens
Lineated Barbet Megalaima lineata
Golden-throated Barbet Megalaima franklinii
Blue-throated Barbet Megalaima asiatica
Blue-eared Barbet Megalaima australis
76
PRATAP SINGH
Forktail 10
Coppersmith Barbet Megalaima haemacephala
Oriental Pied-Hornbill Anthracoceros albirostris
Great Hornbill Buceros bicomis
Brown Hornbill Anorrhinus tickelli
Rufous-necked Hornbill Aceros nipalensis
Wreathed Hornbill Aceros undulatus
Eurasian Hoopoe Upupa epops
Red-headed Trogon Harpactes erythrocephalus
Ward’s Trogon Harpactes wardi
Indian Roller Coracias benghalensis
Dollarbird Eurystomus onentalis
1994
Recent bird records from Arunachal Pradesh
77
Common Kingfisher Alcedo atthis
Stork-billed Kingfisher Pelargopsis capensis
Ruddy Kingfisher Halcyon coromanda
White-throated Kingfisher Halcyon srnymensis
Black-capped Kingfisher Halcyon pileata
Crested Kingfisher Megaceryle lugubris
Pied Kingfisher Ceryle rudis
Blue-bearded Bee-eater Nyctyomis athertoni
Little Green Bee-eater Merops orientalis
Blue-tailed Bee-eater Merops philippinus
Chestnut-headed Bee-eater Merops leschenaulti
Chestnut-winged Cuckoo Clamator coromandus
Large Hawk-Cuckoo Cuculus sparverioides
Common Hawk-Cuckoo Cuculus varius
Indian Cuckoo Cuculus micropterus
Oriental Cuckoo Cuculus saiuratus
Asian Emerald Cuckoo Chrysococcyx maculatus
Violet Cuckoo Chrysococcyx xanthorhynchus
Drongo Cuckoo Sumiculus lugubris
Aslan Koel Eudynamys scolopacea
Green-billed Malkoha Phaenicophaeus tristis
Greater Coucal Ceniropus sinensis
78
PRATAP SINGH
Forktail 10
Lesser Coucal Centropus bengaletisis
Vernal Hanging-Parrot Loriculus vernalis
Grey-headed Parakeet Psittacula finschii
Derbyan Parakeet Psittacula derbiana
Red-breasted Parakeet Psittacula alexandri
Himalayan Swiftlet Collocalia brevirostris
Silver-backed Needletail Hirundapus cochinchinensis
Asian Palm-Swift Cypsiurus balasiensis
Fork-tailed Swift Apus pacificus
Mountain Scops-Owl Otus spilocephalus
Collared Scops-Owl Otus bakkamoena
Eagle-Owl Bubo bubo! bengaletisis
Brown Wood-Owl Strix leptogrammica
Tawny Owl Strix aluco
Collared Owlet Glaucidium brodiei
Asian Barred Owlet Glaucidium cuculoides
Jungle Owlet Glaucidium radiatum
Brown Hawk-Owl Ninox scutulata
Great Eared-Nightjar Eurostopodus macrotis
Grey Nightjar Caprimulgus indicus
Large-tailed Nightjar Caprimulgus macrurus
Indian Nightjar Caprimulgus asiaticus
Rock Pigeon Columba livia
Snow Pigeon Columba leuconota
Speckled Wood-Pigeon Columba hodgsonii
Ashy Wood-Pigeon Columba pulchricollis
1994
Recent bird records from Arunachal Pradesh
79
Oriental Turtle-Dove Streptopelia orientalis
Spotted Dove Streptopelia chinensis
Red Collared-Dove Streptopelia tranquebarica
Eurasian Collared-Dove Streptopelia decaocto
Barred Cuckoo-Dove Macropygia unchall
Emerald Dove Chalcophaps indica
Pompadour Green-Pigeon Treron pompadora
Thick-billed Green-Pigeon Treron curvirostra
Pin-tailed Green-Pigeon Treron apicauda
Wedge-tailed Green-Pigeon Treron sphenura
Green Imperial-Pigeon Ducula aenea
Mountain Imperial-Pigeon Ducula badia
Bengal Florican Eupodotis bengalensis
Brown Crake Amauromis akool
White-breasted Waterhen Amauromis phoenicurus
Black-tailed Crake Amauromis bicolor
Common Moorhen Gallinula chloropus
Eurasian Woodcock Scolopax rusticola
Black-tailed Godwit Limosa limosa
Common Greenshank Tringa nebularia
Green Sandpiper Tringa ochropus
Common Sandpiper Tringa hypoleucos
Great Thick-knee Burhinus recurvirostris
Ibisbill Ibidorhyncha struthersii
Little Ringed Plover Charadrius dubius
Northern Lapwing V anellus vanellus
80
PRATAP SINGH
Forktail 10
River Lapwing Vanellus duvaucelii
Red-wattled Lapwing Vanellus indicus
Small Pratincole Glareola laciea
Great Black-headed Gull Larus ichthyaetus
Brown-headed Gull Larus brunnicephalus
River Tern Sterna aurantia
Black-bellied Tern Sterna acuticauda
Osprey Pandion haliaetus
Jerdon’s Baza Aviceda jerdoni
Oriental Honey-buzzard Pernis ptilorhyncus
Black-winged Kite Elanus caendeus
Black Kite Milvus mi grans
Black-eared Kite Milvus lineatus
White-tailed Eagle Haliaeetus albicilla
Lesser Fish-Eagle Ichthyophaga humilis
Grey-headed Fish-Eagle Ichthyaetus ichthyaetus
White-rumped Vulture Gyps bengalensis
Long-billed Vulture Gyps indicus
Himalayan Griffon Gyps himalayensis
Eurasian Griffon Gyps fulvus
Short-toed Snake-Eagle Circaetus gallicus
Crested Serpent-Eagle Spilomis cheela
Western Marsh-Harrier Circus aeruginosus
Northern Harrier Circus cyaneus
Pied Harrier Circus tnelanoleucos
Crested Goshawk Accipiter trivirgatus
Shikra Accipiter badius
Besra Accipiter virgatus
Eurasian Sparrowhawk Accipiter tiisus
Northern Goshawk Accipiter gentilis
Common Buzzard Buteo buteo
Black Eagle Ictinaetus malayensis
Golden Eagle Aquila chrysaetos
Changeable Hawk-Eagle Spizaetus cirrhatus
1994
Recent bird records from Arunachal Pradesh
81
Mountain Hawk-Eagle Spizaetus nipalensis
Pied Falconet Microhierax melanoleucos
Lesser Kestrel Falco naumanni
Common Kestrel Falco tinnunculus
Amur Falcon Falco amurensis
Merlin Falco columbarius
Eurasian Hobby Falco subbuteo
Oriental Hobby Falco severus
Little Grebe Tachybaptus ruficollis
Great Crested Grebe Podiceps cristatus
Oriental Darter A nhinga melanogaster
Little Cormorant Phalacrocorax tiiger
Indian Cormorant Phalacrocorax fuscicollis
Great Cormorant Phalacrocorax carbo
Little Egret Egretta garzetia
Grey Heron Ardea cinerea
Great Egret Casmerodius albus
Intermediate Egret Mesophoyx intermedia
Cattle Egret Bubulcus ibis
Indian Pond-Heron Ardeola grayii
Striated Heron Butorides striatus
Black-crowded Night-Heron Nycticorax nyciicorax
Cinnamon Bittern Ixobrychus cinnamomeus
Black-headed Ibis Threskiomis melanocephalus
Black Stork Ciconia nigra
Woolly-necked Stork Ciconia episcopus
Black-necked Stork Ephippiorhynchus asiaticus
Lesser Adjutant Leptoptilos javanicus
Silver-breasted Broadbill Serilophus lunatus
Long-tailed Broadbill Psansotnus dalhousiae
82
PRATAP SINGH
Forktail 10
Asian Fairy-bluebird Irena puella
Blue-winged Leafbird Chloropsis cochinchinensis
Golden-fronted Leafbird Chloropsis aurifrons
Orange-bellied Leafbird Chloropsis hardwickii
Brown Shrike Lanius cristatus
Long-tailed Shrike Lanius schach
Grey-backed Shrike Lanius tephronoius
Eurasian Jay Garrulus glandarius
Gold-billed Magpie Urocissa flavirosiris
Green Magpie Cissa chinensis
Rufous Treepie Dendrocitta vagabunda
Grey Treepie Dendrocitta formosae
Collared Treepie Dendrocitta frontalis
Spotted Nutcracker Nucifraga caryocatactes
Red-billed Chough Pyrrhocorax pyrrhocorax
Yellow-billed Chough Pyrrhocorax graculus
House Crow Corvus splendens
Large-billed Crow Corvus macrorhynchos
Ashy Woodswallow Artamus fuscus
1994
Recent bird records from Arunachal Pradesh
83
Slender-billed Oriole Onolus tetiuirostris
Black-hooded Oriole Oriolus xanthomus
Maroon Oriole Oriolus traillii
Large Cuckooshrike Coracina macei
Black-winged Cuckooshrike Coracina melaschistos
Grey-chinned Minivet Pericrocotus Solaris
Long-tailed Minivet Pericrocotus ethologus
Short-billed Minivet Pericrocotus brevirostris
Scarlet Minivet Pericrocotus flammeus
Bar-winged Flycatcher-shrike Hemipus picatus
Yellow-bellied Fantail Rhipidura hypoxantha
White-throated Fantail Rhipidura albicollis
Black Drongo Dicrurus macrocercus
Ashy Drongo Dicrurus leucophaeus
Bronzed Drongo Dicrurus aeneus
Lesser Racket-tailed Drongo Dicrurus remifer
Hair-crested Drongo Dicrurus hotteniotius
Greater Racket-tailed Drongo Dicrurus paradiseus
84
PRATAP SINGH
Forktail 10
Black-naped Monarch Hypothymis azurea
Asian Paradise-Flycatcher Terpsiphone paradisi
Common Iora Aegiihina tiphia
Large Woodshrike Tephrodomis gularis
Common Woodshrike Tephrodomis pondtcerianus
White-throated Dipper Cinclus cinclus
Brown Dipper Cinclus pallasii
Blue-capped Rock-Thrush Monticola cinclorhynchus
Chestnut-bellied Rock-Thrush Momicola rufivemris
Blue Rock-Thrush Monticola solitarius
Blue Whistling-Thrush Myiophonus caeruleus
Orange-headed Thrush Zoothera citrina
Plain-backed T hrush Zoothera mollissima
Long-tailed Thrush Zoothera dixoni
Scaly Thrush Zoothera daurna
Long-billed Thrush Zoothera monticola
Black-breasted Thrush Turdus dissimilis
White-collared Blackbird Turdus albocinctus
Grey-winged Blackbird Turdus boulboul
Chestnut Thrush Turdus rubrocanus
1994
Recent bird records from Arunachal Pradesh
85
Dark-throated Thrush Turdus ruficollis
Lesser Shortwing Brachypteryx leucophrys
White-browed Shortwing Brachypteryx montana
Dark-sided Flycatcher Muscicapa sibirica
Ferruginous Flycatcher Muscicapa ferruginea
Rufous-gorgeted Flycatcher Ficedula strophiata
Red-breasted Flycatcher Ficedula parva
White-gorgeted Flycatcher Ficedula monileger
Snowy-browed Flycatcher Ficedula hyperythra
Little Pied Flycatcher Ficedula ivestermanni
Ultramarine Flycatcher Ficedula superciliaris
Slaty-blue Flycatcher Ficedula tricolor
Verditer Flycatcher Eumyias thalassina
Large Niltava Niltava grandis
Small Niltava Niltava macgrigoriae
86
PRATAP SINGH
Forktail 10
Rufous-bellied Niltava Niltava sundara
Vivid Niltava Niltava vivida
Pale Blue-Flycatcher Cyomis unicolor
Blue-throated Flycatcher Cyomis rubeculoides
Hill Blue-Flycatcher Cyomis banyumas
Tickell’s Blue-Flycatcher Cyomis tickelliae
Pygmy Blue-Flycatcher Muscicapella hodgsoni
Grey-headed Canary-Flycatcher Culicicapa ceylonensis
White-tailed Rubythroat Luscinia pectoralis
Bluethroat Luscinia svecica
Orange-flanked Bush-Robin Tarsiger cyanurus
Golden Bush-Robin Tarsiger chrysaeus
White-browed Bush-Robin Tarsiger indicus
Rufous-breasted Bush-Robin Tarsiger hyperythrus
Oriental Magpie-Robin Copsychus saularis
White-rumped Shama Copsychus malabaricus
Black Redstart Phoenicurus ochruros
Hodgson’s Redstart Phoenicurus hodgsoni
Daurian Redstart Phoenicurus auroreus
White-winged Redstart Phoenicurus erythrogaster
1994
Recent bird records from Arunachal Pradesh
87
White-capped Water-Redstart Chaimarromis leucocephalus 150-3600
Plumbeous Water- Redstart Rhyacomis fuliginosus 120-2700
White-tailed Robin Cinclidium leucurum
Little Forktail Enicurus scouleri
Black-backed Forktail Enicurus immaculatus
Slaty-backed Forktail Enicurus schisiaceus
Thingbu-Mago track 3/6
Tenga-Bomdilla road 8
Chakoo road 8
Nigguing 8
Mayodia 8
Pange 8
Malinye 4
U 6
U 6
Nacho-Choyo-Taksing 6
300-1200 Motijheel track la
Ranijheel 1 a
Sessa ib
400-3500 Thingbu track 6
Orak-Taksing track 6
Dambuin 6
Suchung 6
Hotspring 6
Roing 6
Khari 6
Hunli-Etalin 6
150-700 Khari 6
White-crowned Forktail Enicurus leschenaulti
Spotted Forktail Enicurus maculatus
Purple Cochoa Cochoa purpurea
Green Cochoa Cochoa viridis
Siberian Stonechat Saxicola maura
Grey Bushchat Saxicola ferrea
Spot-winged Starling Saroglossa spiloptera
Chestnut-tailed Starling Stumus malabaricus
Brahminy Starling Stumus pagodarum
Asian Pied Starling Stumus contra
Common Myna Acridotheres tristis
Jungle Myna Acridotheres fuscus
Great Myna Acridotheres grandis
Hill Myna Gracula religiosa
88
PRATAP SINGH
Forktail 10
Chestnut-vented Nuthatch Sitta nagaensis
Chestnut-bellied Nuthatch Sitta castanea
White-tailed Nuthatch Sitta himalayensis
Velvet-fronted Nuthatch Sitta frontalis
Beautiful Nuthatch Sitta formosa
Wallcreeper Tichodroma muraria
Eurasian Tree-creeper Certhia familaris
Bar-tailed T reecreeper Certhia himalayana
Rusty-flanked Treecreeper Certhia nipalensis
Brown-throated Tree-creeper Certhia discolor
Winter Wren Troglodytes troglodytes
Fire-capped Tit Cephalopyrus flammiceps
Rufous- vented Tit Pams rubidiventris
Coal Tit Parus ater
Grey-crested Tit Pams dichrous
Great Tit Pams major
Green-backed Tit Pams monticolus
Yellow-cheeked Tit Pams spilonotus
Yellow-browed Tit Sylvipams modestus
1994
Recent bird records from Arunachal Pradesh
89
Sultan Tit Melanochlora sultanea
Black-throated Tit Aegnhalos concinnus
Black-browed Tit Aegithalos iouschistos
Sand Martin Riparia riparia
Plain Martin Riparia paludicola
Barn Swallow Hirundo rustica
Asian House-Martin Delichon dasypus
Nepal House-Martin Delichon nipalensis
Crested Finchbill Spizixos canifrons
Striated Bulbul Pycnonotus striatus
Black-crested Bulbul Pycnonotus melanicierus
Red-whiskered Bulbul Pycnonotus jocosus
Himalayan Bulbul Pycnonotus leucogenys
Red-vented Bulbul Pycnonotus cafer
White-throated Bulbul Alophoixus flaveolus
Ashy Bulbul Hemixos flavala
Mountain Bulbul Hypsipetes mcclellandii
Black Bulbul Hypsipetes leucocephalus
Zitting Cisticola Cisticola juncidis
Striated Prinia Prinia criniger
Hill Prinia Prinia atrogularis
90
PRATAP SINGH
Forktail 10
Rufescent Prinia Prinia rufescens
Grey-breasted Prinia Prinia hodgsonii
Graceful Prinia Prinia gracilis
Yellow-bellied Prinia Prinia flaviventris
Plain Prinia Prinia inomata
Oriental White-eye Zosierops palpebrosus
Chestnut-headed Tesia Tesia castaneocoronata
Slaty-bellied Tesia Tesia olivea
Grey-bellied Tesia Tesia cyaniventer
Brownish-flanked Bush-Warbler Cettia fortipes
Aberrant Bush-Warbler Cettia flavolivacea
Grey-sided Bush-Warbler Cettia brunnifrons
Mountain Tailorbird Orthotomus cuculatus
Common Tailorbird Orthotomus sutorius
Dusky Warbler Phylloscopus fuscatus
Tickell’s Leaf-Warbler Phylloscopus affinis
Ashy-throated Warbler Phyloscopus maculipennis
Pale-rumped Warbler Phylloscopus chloronotus
Inornate Warbler Phylloscopus inomatus
Greenish Warbler Phylloscopus trochiloides
Large-billed Leaf-Warbler Phylloscopus magnirostris
Eastern Crowned Warbler Phylloscopus coronarus
Blyth’s Leaf-Warbler Phylloscopus reguloides
1994
Recent bird records from Arunachal Pradesh
91
Yellow- vented Warbler Phylloscopus cantator
Golden-spectacled Warbler Seicercus burkii
Grey-hooded Warbler Seicercus xanthoschistos
White-spectacled Warbler Seicercus affinis
Grey-cheeked Warbler Seicercus poliogenys
Chestnut-crowned Warbler Seicercus castaniceps
Broad-billed Warbler Tickellia hodgsotii
Rufous-faced Warbler Abroscopus albogularis
Black-faced Warbler Abroscopus schisticeps
Yellow-bellied Warbler Abroscopus superciliaris
Striated Grassbird Megalurus palustris
Rufous-rumped Grassbird Graminicola bengalensis
White-throated Laughingthrush Garrulax albogularis
White-crested Laughingthrush Garrulax leucolophus
Lesser Necklaced Laughingthrush Garrulax monileger
Greater Necklaced Laughingthrush Garrulax pectoralis
92
PRATAP SINGH
Forktail 10
1994
Recent bird records from Arunachal Pradesh
93
Slender-billed Scimitar-Babbler Xiphirhynchus superciliarisl 200-2400 Tenga-Bomdilla road
94
PRATAP SINGH
Forktail 10
Red-billed Leiothrix Leioihrix lutea
Cutia Cutia nipalensis
Black-headed Shrike-Babbler Ptenithius rufiventer
White-browed Shrike-Babbler Ptenithius flaviscapis
Green Shrike-Babbler Ptenithius xanthochlonis
Black-eared Shrike-Babbler Ptenithius melanotis
White-hooded Babbler Gampsorhynchus rufulus
Rusty-fronted Barwing Actinodura egertoni
Streak-throated Barwing Actinodura waldeni
Blue-winged Minla Minla cyanouroptera
Chestnut-tailed Minla Minla singula
1994
Recent bird records from Arunachal Pradesh
95
Red-tailed Minla Minla ignotincta
Golden-breasted Fulvetta Alcippe chrysoiis
Yellow-throated Fulvetta Alcippe cinerea
Rufous-winged Fulvetta Alcippe castaneceps
White-browed Fulvetta Alcippe vinipectus
Ludlow’s Fulvetta Alcippe ludlowi
Rufous-throated Fulvetta Alcippe rufogularis
Nepal Fulvetta Alcippe nipalensis
Rufous-backed Sibia Heterophasia annectans
Rufous Sibia Heterophasia capistrata
Beautiful Sibia Heterophasia pulchella
96
PRATAP SINGH
Forktail 10
Long-tailed Sibia Heierophasia picaoides
Striated Yuhina Yuhina castaniceps
White-naped Yuhina Yuhina bakeri
Whiskered Yuhina Yuhina flavicollis
Stripe-throated Yuhina Yuhina gularis
Rufous- vented Yuhina Yuhina occipitalis
Black-chinned Yuhina Yuhina nigrimenta
White-bellied Yuhina Yuhina zantholeuca
100-1200 Sesni lb/2b c
Sessa lb/2b c
Tipi 2a c
Ramsing la c
Pasighat la n
Glao Lake track lb/2b c
Deban la c
Miao-Hornbill la/2a c
Mehao lake track lb n
400-1600 Biyonali lb n
Glao Lake track la c
Hornbill la c
Roing 2p n
600-1900 Sesni lb c
Nabha 2b c
Glemu-Reddinglb/ld/2b/2d c
Ramsing la c
Mipi lb/2b c
Glao Lake lb a
Suchung lb c
Hunli-Etalin 2a n
Etalin-Malinye lb/2a/2b n
Sessa lb n
150-2500 Jang-Thingbu track Id c
Khari la c
Limeking 2b c
Glemu-Taksinglb/ld/2b/2d/8 c
Pasighat la/2a c
Alinye lb/2b c
Glao Lake track la c
Milinja lc/ld c
Suchung lb/lc c
Roing-Mayodia 1 b n
Pange lb/ Id n
2400-3200 Thingbu 2f73 n
Bomdilla 2d c
Chakoo Id c
Talley valley le c
Taksing 8 r
Hotspring le c
Mayodia Id n
2400-3400 Broksar Id c
Mago 2f/3 c
Eagle’s Nest le c
Talley valley le c
Taksing 2f78 c
Mayodia Id c
600-2200 Chakoo road lb c
Nabha 2b n
Ramsing la c
Wakro la c
Vijaynagar road la c
Suchung lb/lc c
Etalin-Malinye 2b/8 c
Pange-Talley Valley lb/ld n
Sessa lb n
200-2400 Chakoo road lb r
Tipi la n
Simna Parvat track la n
Talley valley le r
Pango la n
Dambuin lb/lc n
Deban-Hombill la c
Yachuli 2c/8 n
Etalin-Malinye lb n
1994
Recent bird records from Arunachal Pradesh
97
n
n
n
n
n
n
n
n
c
n
n
n
c
c
c
n
c
c
c
n
c
n
c
n
n
n
c
c
c
n
n
r
n
n
n
n
n
r
r
r
c
n
n
n
n
n
n
n
n
c
c
c
c
c
n
c
n
c
c
c
n
c
98
PRATAP SINGH
Forktail 10
Black-throated Sunbird Aethopyga saturate
Crimson Sunbird Aethopyga siparaja
Fire-tailed Sunbird Aethopyga ignicauda
Little Spiderhunter Arachnothera longirostris
Streaked Spiderhunter Arachnothera magna
House Sparrow Passer domesticus
Russet Sparrow Passer rutilans
Eurasian Tree Sparrow Passer montanus
White Wagtail Motacilla alba
White-browed Wagtail Motacilla maderaspatensis
Citrine Wagtail Motacilla citreola
Yellow Wagtail Motacilla flava
Grey Wagtail Motacilla cinerea
Paddyfield Pipit Anthus rufulus
Tawny Pipit Anthus campestris
Olive-backed Pipit Anthus hodgsoni
1994
Recent bird records from Arunachal Pradesh
99
Rosy Pipit Anthus roseaius
Alpine Accentor Prunella collaris
Rufous-breasted Accentor Prunella strophiata
Maroon-backed Accentor Prunella immaculata
Bay a Weaver Ploceus philippinus
White-rumped Munia Lonchura striata
Scaly-breasted Munia Lonchura punctulata
Black-headed Munia Lonchura malacca
Yellow-breasted Greenfinch Carduelis spinoides
Black-headed Greenfinch Carduelis ambigua
Dark-breasted Rosefinch Carpodacus nipalensis
Common Rosefinch Carpodacus erythrinus
Spot-winged Rosefinch Carpodacus rodopeplus
White-browed Rosefinch Carpodacus thura
Beautiful Rosefinch Carpodacus pulcherrimus
Dark-rumped Rosefinch Carpodacus edwardsii
Crimson-browed Finch Pinicola subhimachalus
Scarlet Finch Haematospiza sipahi
Brown Bullfinch Pyrrhula nipalensis
Red-headed Bullfinch Pyrrhula erythrocephala
Grey-headed Bullfinch Pyrrhula erythaca
Collared Grosbeak Mycerobas affinis
Spot-winged Grosbeak Mycerobas melanozanthos
White-winged Grosbeak Mycerobas camipes
Gold-naped Finch Pyrrhoplectes epauletta
Crested Bunting Melophus lathami
Godlewski’s Bunting Emberiza godlewskii
Little Bunting Emberiza pusilla
Yellow-breasted Bunting Emberiza aureola
100
PRATAP SINGH
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Locality codes:
1 Towang
2 Jang-Broksar-Thingbu-Mago-Churna-Chirila track
3 Sella pass
4 Sange
5 Balamau
6 Rowta
7 Dirang
8 Sangti
9 Bomdilla
1 0 Foothills-Doimara-Khellong-Sesni-Bompu-
Chakoo-Eagle’s Nest track
1 1 Sessa
12 Tipi
1 3 Seijusa-Khari-Upper Dikroi track in Pakhui Wildlife
Sanctuary
14 Seijusa
15 Namora
16 Basar Nala-Simna Parvat track
17 Itanagar
18 Chessa
19 Naharlagun
20 Kirsinghsa
21 Doimukh
22 Bandardewa
23 Yachuli
24 Hapoli-Pange-Talley valley track
25 Nacho-Nabha-Limeking-Orak-
Glenshang-Dujbun-Redding-Taksing track
\
Glemu-Choyo-Majha track
26 Daparijo
27 Migging-Pango-Nigguing-Tuting track
-Keegut track
28 Boleng
29 Pangin
30 Ramsing
31 Jengging
32 Sille
33 Pasighat
34 D’Ering Memorial Wildlife Sanctuary
35 Roing
36 Mayodia
37 Etalin-Anini-Alinye-Angrim valley-Dambuin track
/
Mipi-Biyonali-Basad track
38 Malinye
39 Hunli
40 Namsai
41 Deomali
42 Jairampur
43 Tezu
44 Dimbey
45 Wakro-Glao Lake track
46 Hayliang
47 Deban-Vijay Nagar road
48 Wallong-Karoti-Kibitho-Ditchu-Milinja-Simbe-
Hotspring track \
Suchung-Kundav-Para track
49 Miao
50 Motijheel
51 Hornbill
52 Ranijheel
53 Mehao lake
U =ubiquitous
Habitat classification:
1 Primary forests (i.e. undisturbed forests)
la Tropical semi-evergreen and evergreen forests
lb Subtropical broadleaved forests
lc Pine forests
Id Temperate broadleaved forests
le Temperate mixed forests
If Temperate conifer forests
2 Mixed secondary forests
2a Tropical semi-evergreen and evergreen forests
2b Subtropical broadleaved forests
2c Pine forests
2d Temperate broadleaved forests
2e Temperate mixed forests
2f Temperate conifer forests
2p Plantations
2s Succession woodlands
3 Rhododendron-bamboo scrub (in temperate and
alpine zones)
4 Jhum/cultivation/grazing/habitation
5 Swamp/wetland/wet cultivation
6 Waterbody (includes riverbeds and nallas)
7 Grassland of riverine floodplains with scattered
trees
8 Scrubland (degraded forest areas, excludes
rhodendron-bamboo)
9 Alpine vegetation (excludes rhodendron-bamboo
scrub)
10 Earth and rock cliffs
11 Air
Abundance categories:
a Seen very often and in large numbers
c Seen quite often
r Rarely seen
n Abundance not known.
1994
Recent bird records from Arunachal Pradesh
101
Figure 1. Map of localities mentioned in the text.
102
PRATAP SINGH
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APPENDIX 2
OTHER SPECIES RECORDED FROM ARUNACHAL PRADESH
Snow Partridge Lerwa lerwa
Tibetan Snowcock Teiraogallus tibetanus
Buff-throated Partridge Tetraophasis szechenyii
Black Francolin Francolinus francolinus
Snow Partridge Lerwa lerwa
Tibetan Partridge Perdix hodgsoniae
Rufous-throated Partridge A rborophila rufogularis
Mountain Bamboo-Partridge Bambustcola fytchii
’Blyth’s Tragopan Tragopan blyihii
’Sclater’s Monal Lophophorus sclateri
Tibetan Eared-Pheasant Crossoptilon harmani
Lesser Whistling-Duck Dendrocygna javanica
Bean Goose Anser fabalis
Greylag Goose Anser anser
Bar-headed Goose Anser indicus
Red-breasted Goose Branta ruficollis
’White-winged Duck Cairina scutulata
’Pink-headed Duck Rhodonessa caryophyllacea
Red-crested Pochard Netta rufina
Common Pochard Aythya ferina
Long-tailed Duck Clangula hyernalis
Himalayan Flameback Dinopium shorii
Black-rumped Flameback Dinopium benghalense
?Brown-headed Barbet Megalaima zeylanica
’Blyth’s Kingfisher Alcedo hercules
Blue-eared Kingfisher Alcedo meninting
Black-backed Kingfisher Ceyx erithacus
Hodgson’s Hawk-Cuckoo Cuculus fugax
Common Cuckoo Cuculus canorus
Lesser Cuckoo Cuculus poliocephalus
Plaintive Cuckoo Cacomantis merulinus
Sirkeer Malkoha Phaenicophaeus leschenaultii
Slaty-headed Parakeet Psiltacula himalayana
Blossom-headed Parakeet Psittacula roseata
White-throated Needletail Hirundapus caudacutus
Brown-backed Needletail Hirundapus giganteus
Alpine Swift Tachymarptis melba
House Swift Apus nipalensis
Crested Treeswift Hemiprocne coronata
Oriental Bay-Owl Phodilus badius
Oriental Scops-Owl Otus sutiia
Spot-bellied Eagle-Owl Bubo nipalensis
Brown Fish-Owl Ketupa zeylonensis
Spotted Owlet Athene brama
Hodgson’s Frogmouth Batrachostomus hodgsoni
’Pale-capped Pigeon Columba punicea
Orange-breasted Green-Pigeon Treron bicincta
’Black-necked Crane Grus nigricollis
Solitary Snipe Gallinago solitaria
12.36
27
28
9.36
12.36
27
1.2.5.12.17.20.25
37
9.12.36
1, ?2,4,28
7
32
36
15
11
22
2,29,32,37
32
32
1 1,15
30.36
9.36
13
?25
1 1, 12,17,20,745
17.36
17.36
?24,?25,36
1 1.15.17.28
11.25
24
36
36
2, ?25
12.17.25.28
1 1.12.25
36
24.25.36
2
12,13
36
9.12.36
17
25.36
13.36
1,2
17.36
10,1 1,38
12.36
1994
Recent bird records from Arunachal Pradesh
103
*Wood Snipe Galltnago nemoricola 27
Common Snipe Gallinago gallinago 1 j
Marsh Sandpiper Tringa stagnatilis 26
Wood Sandpiper Tringa glareola 29
Long-billed Plover Charadrius placidus 28
Oriental Pratincole Glareola maldivarum 2
Little Gull Larus minutus 1 5
Black Baza Aviceda leuphotes 36
Brahminy Kite Haliastur indus 29
*Pallas’s Sea-Eagle Haliaeetus leucoryphus 2
Lammergeier Gypaetus barbatus 26,36
Red-headed Vulture Sarcogyps calvus 29
Rufous-bellied Eagle Hieraaeius kienerii 9,12,26,36
Collared Falconet Microhierax caemlescens 36
Peregrine Falcon Falco peregrinus 13,36
Black-necked Grebe Podiceps nigricollis 25
Goliath Heron Ardea goliath 1 7
* White- bellied Heron Ardea insignis 12,16
Purple Heron Ardea purpurea 29
Chinese Pond-Heron Ardeola bacchus 17
Blue-naped Pitta Pitta nipalensis 1 ,2,5, 1 1 , 1 2, 1 7
Blue Pitta Pitta cyanea 25,36
Hooded Pitta Pitta sordida 11,12
Indian Pitta Pitta brachyura 36
Common Raven Corvus corax 27
Black-winged Cuckoo-shrike Coracina melaschistos 1,2,1 1,17,24,25
Rosy Minivet Pericrocotus roseus 24,36
Small Minivet Pericrocotus cinnamomeus 1 7
Crow-billed Drongo Dicmrus annectans 17,36
Pied Thrush Zoothera wardii 9,36
Dark-sided Thrush Zoothera marginata 17,36
Tickell’s Thrush Turdus unicolor 1 1
Eurasian Blackbird Turdus memla 27
Eyebrowed Thrush Turdus obscums 26,36
Dusky Thrush Turdus naumanni 36
Gould’s Shortwing Brachypteryx stellata 27,28
*Rusty-belued Shortwing Brachypteryx hyperythra 17,25,36
Slaty-backed Flycatcher Ficedula hodgsonii 28,45
Sapphire Flycatcher Ficedula sapphira 1 , 1 7,25
Pale-chinned Flycatcher Cyomis poliogenys 25,36
Firethroat Luscinia pectardens 25
Indian Blue Robin Luscinia bmnnea 25,36
White-throated Redstart Phoenicums schisticeps 9,36
White-bellied Redstart Hodgsonius phaenicuroides 9,36
Blue-fronted Robin Cinclidium frontale 37
Grandala Grandala coelicolor 36
Jerdon’s Bushchat Saxicola jerdoni 36
Golden-crested Myna Ampeliceps coronatus 17
Wire-tailed Swallow Himndo smithii 29
Red-rumped Swallow Himndo daurica 1 2, 17,36
Goldcrest Regulus regulus 9,36
Golden-headed Cisticola Cisticola exilis 29,36
Pale-footed Bush-Warbler Cettia pallidipes 2,?1 1
Chestnut-crowned Bush-Warbler Cettia major 27
Yellowish-bellied Bush-Warbler Cettia acanthizoides 28
104
PRATAP SINGH
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Spotted Bush-Warbler Bradypterus thoracicus
Brown Bush-Warbler Bradypterus luteoveturis
Paddyfield Warbler Acrocephalus agricola
Thick-billed Warbler Acrocephalus aedon
Smoky Warbler Phylloscopus fuligiventer
Buff-barred Warbler Phylloscopus pulcher
Spot-breasted Laughingthrush Garrulax merulinus
Scaly Laughingthrush Garrulax subunicolor
Buff-breasted Babbler Pellomeum lickelli
Spot-throated Babbler Pellomeum albiventre
Large Scimitar-Babbler Pomatorhinus hypoleucos
Spot-breasted Scimitar-Babbler Pomatorhinus erythrocnemis
* Rusty-throated Wren-Babbler Spelaeomis badeigularis
Yellow-eyed Babbler Chrysomma sinense
Slender-billed Babbler Turdoides longirostris
Jungle Babbler Turdoides striatus
Streak-throated Fulvetta Alcippe cinereiceps
Rusty-capped Fulvetta Alcippe dubia
Grey Sibia Heterophasia gracilis
‘Black-breasted Parrotbill Paradoxomis flavirostris
Fulvous Parrotbill Paradoxomis fulvifrons
Horned Lark Eremophila alpestris
Yellow-bellied Flowerpecker Dicaeum melanoxanthum
Orange-belued Flowerpecker Dicaeum trigcnostigma
Pale-billed Flowerpecker Dicaeum erylhrorhynchos
Forest Wagtail Dendronanthus indicus
Rufous-streaked Accentor Prunella himalayana
Robin Accentor Prunella rubeculoides
Tibetan Serin Serinus thibetanus
Plain Mountain-Finch Leucosticte nemoricola
Crimson Rosefinch Carpodacus rubescens
Red-fronted Rosefinch Carpodacus puniceus
Red Crossbill Loxia curvirostra
Chestnut-eared Bunting Emberiza fucata
Chestnut Bunting Emberiza rutila
1,27
28
17
17
9,36
9.36
1,17
1,2,13,28,48
2,5,12,13,17,20,24,35,45
1.2.25
12.17.20.36
36
2,34
17
36
13.36
37
12.17.20.25
3.36
9.36
28
36
9,36
36
36
17
9,36
26
36
17,28
28
9,36
36
36
37
1994
FORKTAIL 10 (1994): 105 - 1 14
105
Birds of Rajaji National Park, India
S. PANDEY, JUSTUS JOSHUA, N. D. RAI, D. MOHAN, G. S.
RAW AT, K. SANKAR, M. V. KATTI, D. V. S. KHATI and
A. J. T. JOHNSINGH
INTRODUCTION
Rajaji National Park (29°51’7"N to 30°15’5"N and 77°57’7"E to 78°23’36" E) is situated in the
Shiwalik hills and outer Himalaya of Uttar Pradesh state of India. It is 820.2 km- in area and it spreads
over the civil districts of Dehra Dun, Haridwar and Garhwal (Fig. 1). The tract is mainly hilly,
traversed by a number of steep ridges and valleys alternating with each other. The river Ganges bisects
the park.
STUDY AREA
The area to the west of the Ganges belongs to the Shiwalik chain of
mountains and has a prominent north-west south-east ridge running
through the middle of it. The area north of this ridge slopes gently into the
Dehra Dun valley and is covered with dense Sal Shorea robusta forests.
Champion and Seth (1968) classified it as Moist Shiwalik Sal Forest. The
area south of the ridge has a jagged topography with a number of steep ridges
which emerge from the main Shiwalik ridge and have narrow valleys
between them, housing seasonally swift rivers locally called ‘Rau’ (dried
river bed) . The ridges are grassy with scattered tree growth. A strip of forest
on flat ground forms the southern boundary of the park. The forest on the
south of the main ridge can be termed as Dry Shiwalik Sal Forest according
to Champion and Seth (1968). Anogeissus latifolia is abundant on slopes,
associated wth Sal in some places. The area east of the Ganges does not have
a well defined main ridge. The northern part of this area belongs to the outer
Himalaya. Numerous ridges run in various directions and there are some
elevated flat areas. In general the forest varies from moist to dry and from
mixed to nearly pure Sal forest, depending on the aspect and slope.
A substantial area of the park is comprised of river beds which remain dry
for the greater part of the year. Some areas are under plantations of Ailanthes
excelsa, Tectona grandis, Haplophragma etc. There is a barrage on the River
Ganges near Haridwar city. The backwaters of the reservoir, as well as a
small stretch of the river Ganges, lie in the national park. These water bodies
attract a lot of resident and migratory waterbirds.
Rajaji has a typical continental climate, characterized by a distinct
summer (March-June) and winter (October-February). The temperature
106
S. PANDEY et al.
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Figure 1. Rajaji National Park, India
varies from -1°C in winter to 44°C in summer. The average annual rainfall
is around 2,000 mm, with most of it occurring during the south-west
monsoon from July to September.
1994
Birds of Rajaji National Park, India
107
METHODS
Research on the contemporary status of the avifauna of Rajaji is lacking. In
the first half of this century a comprehensive bird list for the Dehra Dun
valley was prepared by Osmaston (1935). Dr Salim Ali and Dillon Ripley
have made observations on the avifauna in Doon valley (Ali and Ripley
1983). The present bird records span a period of seven years (1986-1992).
S.P. initiated the bird observations with A.J.T.J. in August-September
1986. Rai (1991) worked on bird species diversity in Rajaji N.P. as a part
of his M.Sc. dissertation. J.J. has carried out observations in the National
Park since 1989, covering all seasons and most of the areas. Other members
have been contributing their observations from birding trips to Rajaji, which
is only 20 km from the Wildlife Institute of India, Dehra Dun.
RESULTS
A total of 312 bird species has been recorded. Of these, 144 are residents,
89 are migrants, 53 are altitudinal migrants, 8 are local migrants and the
status of the remaining 18 is unknown. Some species of birds are at the
western edge of their distribution in Rajaji: Great Hornbill Buceros bicomis
and Golden-fronted Leafbird Chloropsis aurifrons. The Green Magpie Cissa
chinensis has been reported from forest adjoining the Rajaji National Park,
an area which links it with Corbett National Park. The number of sightings
for 20 birds are very high, 1 1 2 birds were seen quite regularly and 1 80 birds
were seen intermittently. Four main parameters, i.e. habitat types, frequency
of observation, migration status and season of observation were recorded at
the time of making observations on birds in the field. The bird list appended
has details of all these aspects.
REFERENCES
Ali, S. and Ripley, S. D. (1983) Handbook of the birds of India and Pakistan. Compact Edition. New
Delhi: Oxford University Press.
Champion, H. G. and Seth, S. K. (1968) A revised survey of the forest types of India. New Delhi:
Government of India.
Osmaston, B. B. (1935) Birds of Dehra Dun and adjacent hills. Indian Military Acad. J. June 1935,
supplement.
Rai, N. D. (1991). A study of heterospecific flocking and nonbreeding bird community structure of
Rajaji National Park, Dehra Dun. M.Sc. dissertation submitted to Saurashtra University, Rajkot
(Gujarat), India. Unpublished.
S. Pandey, Justus Joshua , N. D. Rai, G. S. Razvat, K. Sankar, M. V. Katti and A. J. T. Johnsingh,
Wildlife Institute of India, Post Box No. 18, Dehra Dun-248 001, U.P., India.
D. Mohan, Dy. Director, Nanda Devi Biosphere Reserve, Gopeshwar (Chamoli), U.P., India.
D. V. S. Khati, Director, Rajaji National Park, Shiwalik House, 5-Ansari Road, Dehra Dun, India.
108
S. PANDEY etal.
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APPENDIX 1
BIRDS SEEN IN RAJAJI NATIONAL PARK 1986-1992
Black Francoun Francolinus francolinus
Grey Francolin Francolinus pondicerianus
Jungle Bush-Quail Perdicula asiatica
Red Spurfowl Galloperdix spadicea
Red Junglefowl G alius gallus
Kalij Pheasant Lophura leucomelanos
Indian Peafowl Pavo cristatus
Ruddy Shelduck Tadorna ferruginea
Falcated Duck Anas falcata
Eurasian Wigeon Anas penelope
Mallard Anas platyrhynchos
Spot-billed Duck Anas poecilorhyncha
Northern Shoveler Anas clypeata
Northern Pintail Anas acuta
Common Teal Anas crecca
Red-crested Pochard Netta rufina
Common Pochard Aythya ferina
Ferruginous Pochard Aythya nyroca
Tufted Duck Aythya fuligula
Common Merganser Mergus merganser
Eurasian Wryneck Jynx torquilla
Grey-capped Woodpecker Dendrocopos canicapillus
Fulvous-breasted Woodpecker Dendrocopos macei
Yellow-crowned Woodpecker Dendrocopos mahrattensis
Rufous Woodpecker Celeus brachyurus
Lesser Yellownape Picus chlorolophus
Streak-throated Woodpecker Picus xanthopygaeus
Grey-headed Woodpecker Picus canus
Himalayan Flameback Dinopium shorii
Black-rumped Flameback Dinopium benghalense
Greater Flameback Chrysocolaptes lucidus
White-naped Woodpecker Chrysocolaptes festivus
Great Barbet Megalaima virens
Brown-headed Barbet Megalaima zeylanica
Lineated Barbet Megalaima lineata
Blue-throated Barbet Megalaima asiatica
Coppersmith Barbet Megalaima haemacephala
Indian Grey-Hornbill Ocyceros birostris
Oriental Pied-Hornbill Anthracoceros albirostris
Great Hornbill Buceros bicomis
Eurasian Hoopoe Upupa epops
Indian Roller Coracias benghalensis
Dollarbird Eurystomus orientalis
Common Kingfisher Alcedo atthis
Stork-billed Kingfisher Pelargopsis capensis
White-throated Kingfisher Halcyon smyrnensis
Crested Kingfisher Megaceryle lugubris
Pied Kingfisher Ceryle rudis
Blue-bearded Bee-eater Nyctyomis athertoni
1994
Birds of Rajaji National Park, India
109
Little Green Bee-eater Merops orientalis
Blue-tailed Bee-eater Merops philippinus
Chestnut-headed Bee-eater Merops leschenaulti
Pied Cuckoo Oxylophus jacobinus
Common Hawk-Cuckoo Cuculus varius
Indian Cuckoo Cuculus micropierus
Common Cuckoo Cuculus canorus
Lesser Cuckoo Cuculus poliocephalus
Grey-bellied Cuckoo Cacomantis passerinus
Drongo Cuckoo Sumiculus lugubris
Aslan Koel Eudynamys scolopacea
Sirkeer Malkoha Phaenicophaeus leschenaultii
Greater Coucal Centropus sinensis
Alexandrine Parakeet Psiitacula eupatria
Rose-ringed Parakeet Psittacula krameri
Slaty-headed Parakeet Psittacula himalayana
Plum-headed Parakeet Psittacula cyanocephala
Alpine Swift Tachymarptis melba
Little Swift Apus affinis
Crested Treeswift Hemiprocne coronata
Rock Eagle-Owl Bubo bengalensis
Brown Fish-Owl Ketupa zeylonensis
Jungle Owlet Glaucidium radiatum
Spotted Owlet Athene brama
Brown Hawk Owl Ninox scutulata
Grey Nightjar Caprimulgus indicus
Large-tailed Nightjar Caprimulgus macrurus
Indian Nightjar Caprimulgus asiaticus
Savanna Nightjar Caprimulgus affinis
Rock Pigeon Columba livia
Oriental Turtle-Dove Streptopelia orientalis
Laughing Dove Streptopelia senegalensis
Spotted Dove Streptopelia chinensis
Red Collared-Dove Streptopelia tranquebarica
Eurasian Collared-Dove Streptopelia decaocto
Emerald Dove Chalcophaps indica
Yellow-footed Green-Pigeon Treron phoenicoptera
White-breasted Waterhen Amauromis phoenicurus
Common Moorhen Gallinula chloropus
Common Coot Fulica atra
Common Redshank Tringa totanus
Common Greenshank Tringa nebularia
Nordmann’s Greenshank Tritiga guttifer
Green Sandpiper Tringa ochropus
Wood Sandpiper Tringa qlareola
Common Sandpiper Tringa hypoleucos
Little Stint Calidris minuta
Eurasian Thick-knee Burhinus oedicnemus
Great Thick-knee Burhinus recurvirostris
Black-winged Stilt Himantopus himantopus
Little Ringed Plover Charadrius dubitis
Northern Lapwing Vanellus vanellus
River Lapwing Vanellus duvaucelii
Red-wattled Lapwing Vanellus indicus
Small Pratincole Glareola lactea
Yellow- legged Gull Larus cachinnans
Brown-headed Gull Lams bmnnicephalus
Black-headed Gull Larus ridibundus
no
S. PANDEY el al.
Forktail 10
River Tern Sterna aurantia
Little Tern Sterna albifrons
Black-bellied Tern Sterna acuticauda
Osprey Pandion haliaetus
Oriental Honey-buzzard Pemis ptilorhyncus
Black-winged Kite Elanus caeruleus
Black Kite Milvus migrant
Pallas’s Sea-Eagle Haliaeetus leucoryphus
Lesser Fish-Eagle Ichthyophaga humilis
Egyptian Vulture Neophron percnopterus
White-rumped Vulture Gyps bengalensis
Long-billed Vulture Gyps indicus
Himalayan Griffon Gyps himalayensis
Eurasian Griffon Gyps fulvus
Cinereous Vulture Aegypius monachus
Red-headed Vulture Sarcogyps calvus
Short-toed Snake-Eagle Circaetus gallicus
Crested Serpent-Eagle Spilomis cheela
Western Marsh-Harrier Circus aeruginosus
Shikra Accipiter badius
Eurasian Sparrowhawk Accipiter nisus
Northern Goshawk Accipiter gentilis
White-eyed Buzzard Butastur teesa
Black Eagle Ictinaetus malayensis
Lesser Spotted Eagle Aquila pomarina
Greater Spotted Eagle Aquila clanga
Changeable Hawk-Eagle Spizaetus cirrhatus
Common Kestrel Falco tinnunculus
Peregrine Falcon Falco peregrinus
Little Grebe Tachybaptus ruficollis
Great Crested Grebe Podiceps cristatus
Oriental Darter Anhinga melanogaster
Little Cormorant Phalacrocorax niger
Indian Cormorant Phalacrocorax fuscicollis
Great Cormorant Phalacrocorax carbo
Little Egret Egretta garzetta
Grey Heron Ardea cinerea
Purple Heron Ardea purpurea
Great Egret Casmerodius albus
Intermediate Egret Mesophoyx intermedia
Cattle Egret Bubulcus ibis
Indian Pond-Heron Ardeola grayii
Striated Heron Butorides striatus
Black-crowned Night-Heron Nycticorax nycticorax
Painted Stork Mycteria leucocephala
Black Stork Ciconia nigra
Black-necked Stork Ephippiorhynchus asiaticus
Indian Pitta Pitta brachyura
Golden-fronted Leafbird Chloropsis aurifrons
Orange-bellied Leafbird Chloropsis hardwickii
Isabelline Shrike Lanius isabellinus
Bay-backed Shrike Lanius vittatus
Long-tailed Shrike Lanius schach
Northern Shrike Lanius excubitor
Gold-billed Magpie Urocissa flavirosvris
Blue Magpie Urocissa erythrorhyncha
Green Magpie Cissa chinensis
Rufous T reepie Dendrocitta vagabunda
1994
Birds of Rajaji National Park, India
111
112
S. PANDEY et al.
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1994
Birds of Rajaji National Park, India
113
A = Aquatic
R = Raus (dried river bed)
G = Grass
S = Sal Shorea robusta forest
D = Disturbed (human settlements and cultivation) and open areas
HM = Hills with mixed forests
P = Plantation
SC = Scrubland
RG = Raus and grassy banks
SA = Shorea and Anogeissus mixed.
Abundance Rating:
1 = Birds seen intermittently
2 = Birds seen quite regularly
3 = Birds with very high sightings
Migration Status:
M = Migrant
R = Resident
LM = Local Migrant
AM = Altitudinal Migrant
? = Status not known
114
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1994
FORKTAIL 10 (1994): 1 15 - 130
115
Ornithological survey of Nanda Devi
National Park, India
R. SANKARAN
The ornithological findings of a 52 day multi-disciplinary expedition, carried out from 2 May to 22
June 1993, are presented. Nanda Devi National Park is perhaps the only protected area in the
Himalaya where both geographical inaccessibility and Government policy has resulted in the area
being protected totally from human use since 1982. This is in contrast to former years when excessive
mountaineering and trekking pressures had a negative impact on the ecosystem. This paper
documents the avifauna of the area and compares changes in the abundance of certain species with
data available from previous years. Total protection has apparently resulted in a significant increase
in the populations of certain species of avifauna.
INTRODUCTION
The Himalaya is perhaps the richest biogeographic zone in India. In all, the
Himalaya cover 422,200 km2 (nearly 13% of India’s land surface), and have
been classified into north-western, western, central, eastern and trans-
Himalaya. Of these the trans-Himalaya occupy the largest area (186,200
km2 or 44%), while the rest range from 12,000 km2 (or 3%) to 83,000 km2
(19%). Within this vast and diverse biogeographic zone exists a protected
area network that consists of 58 wildlife sanctuaries and national parks,
covering an area of 12,539 km2 (less than 3%). The western Himalaya have
17 protected areas covering 3,885 km2 (5%) of its area. Nanda Devi
National Park and Biosphere Reserve is an important protected area of this
zone.
Nanda Devi at 7,8 1 7 m is India’s second highest mountain. Conservation
efforts in this area began in 1939 when the entire Rishi Ganga basin was
declared a sanctuary. However, Nanda Devi and the 20 odd mountains
within or rimming the basin were extremely popular to mountaineers and
trekkers. As a consequence of the excessive human pressures, primarily
from mountaineers and trekkers, this area was closed to all human activity
in 1982, when the Nanda Devi National Park was created (Khacher 1983).
In 1988, the area surrounding the National Park was declared a Biosphere
Reserve. While the buffer zone of the Biosphere Reserve was to be an area
of multiple use, the core, Nanda Devi National Park, was to continue to
remain inviolate.
Base line information on the flora and fauna of the Nanda Devi National
Park exists from surveys done at about the time of the ban on human use
(Lamba 1987, Hajra 1983). Thus Nanda Devi is a fascinating and unique
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Figure 1. Nanda Devi National Park
1994
Birds of Nanda Devi National Park, India
1 17
example of the effect of absolute protection on the flora and fauna of the
Himalaya. In 1 993, the Ministry of Environment, Govt, of India, sponsored
a survey by a multidisciplinary team comprised of two botanists, a
mammalogist, an ornithologist, an entomologist and an environmentalist,
with logistic support by the Corps of Engineers (Indian Army), to assess the
effect of 12 years of absolute protection on the flora and fauna. I report the
findings of the ornithological aspects of the survey.
I had two objectives: a) to prepare a comprehensive list of the avifauna
with specific reference to the habitats and altitudes they occurred at, and b)
to assess the status of Galliformes.
STUDY AREA
The Nanda Devi Biosphere Reserve (Fig. 1) is situated in the Kumaon and
Garhwal region of the western Himalaya, in the civil districts of Chamoli,
Pithoragarh and Almora (7 9° 1 0'-80°05 ’E and 30° 1 7'-30° 1 1 ’N) . It covers an
area of 2,236.74 km2, with an inner core zone, essentially the Nanda Devi
National Park (624.62 km2) and an outer buffer zone of 1,612. 12 km2. The
buffer zone has 15 inhabited villages with a population of less than 2,500.
Thus biotic pressures are minimal in this area. Access to Nanda Devi
National Park is very difficult, due to a series of high ridges with peaks such
as Lata, Jhandidhar, Dunagiri, Kalanka, Rishiparvat, Nanda Devi East,
Nanda Khat, Trisul etc., which also form the boundary of the core zone.
Thus, not only is Nanda Devi protected by law, but geographic features act
as an effective (though surmountable) obstacle to human and livestock
entry.
FIELD METHODS AND DATA COMPILATION
This survey lasted for 52 days, from 2 May to 22 June 1993. The amount
of time spent in the three main habitat types (see below) was approximately
19 days in the alpine zone (above 3,800 m), 25 days in the subalpine and
alpine zone (about 3,000-4000 m) and 8 days in the temperate zone (2,200-
3000 m). In addition to this there were three field visits to the temperate
forest above Joshimath. Of the three habitat types, the least field time was
spent in the temperate zone.
Notes were maintained on all species of birds seen, particularly of the
habitats and locations in which they occurred. No attempt was made to
measure densities of the avifauna because there was insufficient time to lay
transects or carry out a sufficient number of repetitions. However, an
abundance ranking is given for the species seen, based on confirmed
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R.SANKARAN
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sightings or calls heard. In the abundance ranking, a flock was considered
as a single sighting.
A simple classification of habitat types was made. Alpine meadows
consisted of tree-less alpine grasslands, where woody species were mainly
juniper Juniperus and dwarf rhododendron Rhododendron anthopogon.
Subalpine forest was dominated by Himalayan Birch Betula utilis, Himalayan
Silver Fir Abies spectabilis, or rhododendron R. campanulatum. Temperate
forests were dominated by oak Quercus, Blue Pine Pinus wallichiana,
Himalayan Yew Taxus baccata ssp. wallichiana and maple Acer. Water
courses included rivers, streams and glacial lakes. Cliffs were steep (>80
steep) mountain sides usually rocky, and boulder-strewn slopes with sparse
vegetation that occurred in the alpine zone and consisted of gentler slopes
(20-40 slopes) predominantly covered with large boulders.
Altitudes were compiled from 1: 50,000 scale Survey of India maps.
Distances were measured using a pedometer whose setting had been
adjusted for relatively small strides.
All birds noted during the survey from Joshimath onwards have been
included. The primary reason for this is that temperate oak forest that is
present in the NDBR did not occur on the route that this expedition took.
The only temperate oak forest that I was able to look at was that above
Joshimath en route to Auli. It is presumed that bird species that occurred at
Auli would occur within those areas of the NDBR which have temperate oak
forest. Furthermore, it was important to compare bird assemblages in
habitats which are perhaps used for wintering and lie outside NDNP.
The status of Galliformes was assessed using two methods. Encounter
rates (number of individuals sighted or heard per km walk) were estimated
for species that were frequently seen or heard and this provided a comparative
index of abundance in different localities. The paths taken are given in Map
2. The other method was to record all sightings and calls heard and present
it as a total (Table 3), inclusive of repeat counts over subsequent field visits.
RESULTS AND DISCUSSION
Distribution patterns
During this survey, a total of 1 12 species was recorded, of which 83 were
recorded within the NDBR and 29 were recorded around Joshimath and the
oak forest at Auli (Appendix 1).
There are four earlier expeditions from which bird lists are available for
this area (Casebolt 1979, Reed 1979, Halberg and Petersen 1984, Tak and
Kumar 1987).
During this survey seven major habitat types were surveyed. Species
1994
Birds of Nanda Devi National Park, India
119
Table 2. Distribution of bird species according to altitude
richness was highest in temperate forests with 47 species, 24 of which were
seen only in this habitat (Table 1). The species richness of temperate forests
is likely to be much higher as this was the least surveyed of all habitat types.
Birds were apparently most abundant in this habitat type. Subalpine forest
ranked the next highest in species richness with 43 species recorded, 18 of
which were only seen in that habitat type. This habitat type, along with
alpine meadows, were the most intensively surveyed areas. Thirty-two
species were recorded in alpine meadows, of which 9 were seen exclusively
in this habitat type.
Of the 111 species recorded, 42 (37%), were seen exclusively in forest
dominated by oak, fir, birch or rhododendron and 9 (8.7%) were exclusive
to alpine meadows. Only 20 species (8 exclusively) were recorded in
degraded forest and agricultural land. This could indicate that the majority
of the species in the areas surveyed are specialists that require primary forest
cover. I could not examine alpine meadows that are subjected to human
activity and thus am unable to assess the impact of degradation/disturbance
on the avifauna of that habitat type.
There was a significant decline in species richness (and apparently of
abundance) as elevation increased (Table 2). Only one species spanned the
entire altitudinal range: the Brown Dipper Cinclus pallasi, of which I had a
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glimpse at the lake at base camp. The decline in species richness with
increasing altitude is concurrent with the distributional patterns of avifauna
with habitat (Table 1). Temperate forests generally occurred below 2,800
m, subalpine forests between 3,000 and 3,800 m and alpine meadows
between 3,800 and 5,000 m.
Notes on the observed movement patterns of birds
Our survey began during very early spring and ended by early summer. This
perhaps accounted for the absence of many species of birds which I had
expected to see, for example buntings Emberiza. On 2 May, when the survey
commenced, leafing of birch (the dominant subalpine tree) had only just
begun, and it even snowed occasionally. It was obvious that the immigration
into alpine and subalpine areas had only just commenced. The most
abundant of the first arrivals appeared to be Phylloscopus warblers, Black-
crested Tits Parus melanolophus, Yellow-bellied Fantails Rhipidura
hypoxantha, Orange-flanked Bush-Robins Tarsiger cyanurus, Blue-fronted
Redstarts Phoenicurus frontalis , Olive-backed Pipits Anthus hodgsoni and
Rosy Pipits Anthus roseatus. Three species of corvids, Yellow-billed Chough
Pyrrhocorax graculus , Red-billed Chough P. pyrrhocorax and Large-billed
Crow Corvus macrorhynchos, and one pigeon, the Snow Pigeon Columba
leuconota, were commonly seen.
Abundance of avifauna was low and, though territories were being
established (e.g. Black-crested Tits were exceedingly vocal at Dibrugeta),
this appeared to be an inconsistent activity among species generally. Many
birds seemed to cover larger areas in search of food e.g. the Yellow-bellied
Fantail. Some species, notably the tits (Green-backed and Black-crested)
and the Orange-flanked Bush-Robin had commenced nesting, as was
evidenced by individuals observed with nesting material (hair and fur of
Himalayan Tahr Hemitragus jemlahicus and Himalayan Musk Deer Moschus
chrysogaster) . I had expected to see a substantial change in species richness
with the onset of warmer weather and the emergence of vegetation, but this
did not occur. The only apparent change was a considerable increase in bird
abundance, but species richness did not increase dramatically. Later arrivals
(some of which occurred earlier in low numbers) included some species of
rosefinch Carpodacus (e.g. Common Rosefinch C. erythrinus) and the
Spotted Nutcracker Nucifraga caryocatactes, the latter being the most
conspicuous late immigrant. Some Phylloscopus warblers also appeared to
immigrate into subalpine forests later, for instance the Large-billed Leaf-
Warbler P. magnirostris. En route to Sarsonpatal, this species was recorded
only at Deodi, in the subalpine birch/fir forest, alongside the Rishi Ganga
river, on 17-19 May. During the return journey, I found this species to be
common at Dibrugeta. Similarly, from 7-16 May I had only one sighting of
1994
Birds of Nanda Devi National Park, India
121
the Chestnut-crowned Bush- Warbler Cettia majorat Dibrugeta, while from
13-16 June I came across this species seven or eight times. The Chestnut-
crowned Bush-Warbler was also interesting because it only occurred in a
very small patch (< 10 ha.) of alpine meadow with cotton easter and rose
Rosa bushes.
Why was there an absence of significant change in the species richness as
summer progressed? One explanation is that the subalpine forests of NDNP
are cut off from forested areas of lower elevations by a ring of high mountains
of over 4,500 m. The only forested inlet into the core area is in the Rishi
Ganga gorge and this is not contiguous. This lack of suitable habitat through
which to move could perhaps be why many species, for example
laughingthrushes, do not ascend to the subalpine forests within the core
area.
Status of Galliformes
The Himalaya have about 26 species of gallinaceous birds (Ali and Ripley
1983). During this survey four species: Snow Partridge Lerwa lerwa,
Himalayan Snowcock Tetraogallus himalayensis, Himalayan Monal
Lophophorus impejanus and Koklass Pheasant Pucrasia macrolopha were
seen, and three more species: Chukar Alectoris chukar, Kalij Pheasant
Lophura leucomelanos and Cheer Pheasant Catreus wallichii were reported.
The sightings (Table 3) are compared with the data collected by Zoological
Survey of India surveys made during 1981-1984 (Table 4). Because Lamba
(1987) did not state the location of sightings, I have compared only total
numbers recorded.
1 . Snow Partridge Lerwa lerwa. I heard this bird twice at Dibrugeta in the
rocky area above the meadow at an altitude of about 4,000 m. I presumed
that a covey of 4-6 birds occurred there. One individual was sighted beyond
‘Sath Kula’, en route to Lata Kharak. I believe this species to be uncommon
in NDNP, though Khacher (1978) found them to be ‘plentiful’.
2. Himalayan Snowcock Tetraogallus himalayensis. This bird was frequently
seen from Pathalkhan (4,100 m) onwards, and occurred as high as Camp
2 (5,900 m) on the Nanda Devi mountain. I found them to be very shy and
those birds that were flushed at Sarsonpatal invariably flew across the river
and landed on the steep rocky cliffs at the base of the Nanda Devi. They
occurred at similar densities in the North Sanctuary (T able 3) . A comparison
of data reveals a significant change in the population of this species between
1981/1984 and 1993 (Table 4). I attribute this change to the total lack of
human-related disturbance.
Some expeditions have reported the presence of Tibetan Snowcock
Tetraogallus tibetanus in NDNP (Reed 1979, Casebolt 1979), and Ali and
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Table 3 Status of Galliformes in Nanda Devi National Park
Table 4 Comparison of sightings of Galliformes in NDNP
Ripley (1983) have said that the range includes Nanda Devi. None of the
individuals that I had a good look at was Tibetan Snowcock. However, the
birds around Base Camp seemed to have slightly different calls from those
at Sarsonpatal. The existence of Tibetan Snowcock in NDNP needs
confirmation.
3. Western Tragopan Tragopan melanocephalus. Tak and Kumar (1987)
suspected the presence of this bird in NDNP. I did not see or hear any and
1994
Birds of Nanda Devi National Park, India
123
inquiries amongst the locals did not result in any information on this species.
I believe that this species does not exist in NDNP. It is the rarest pheasant
in the western Himalaya (Gaston et al. 1981) and its range apparently ends
west of Nanda Devi (Ali and Ripley 1983).
4. Himalayan Monal Lophophorus impejanus. This pheasant was the most
common galliform in NDNP. Ten or more males could be sighted at
Dibrugeta meadow in the early morning or late evening. Females were less
frequently seen, perhaps because nesting had commenced. (One female
with chicks was seen en route to Bethartoli on 20 May 1993; V. K. Pangtey
pers. comm.). Himalayan Monal were less frequently seen elsewhere in
NDNP, but a few occurred at the tree line throughout the survey route,
except at Bhujgara. The lowest altitude Monal was seen was at Belta Kharak
(2,800 m), where two females and one male were sighted and were heard a
few times.
There has been a distinct increase in the population of Himalayan Monals
in NDNP. Between 1 98 1 and 1 984 six expeditions, totalling 1 67 days, were
made to NDNP by Tak and Kumar (1987). Only 63 individuals were
sighted by them (Lamba 1987), whereas in less than 35 days in suitable
habitat, I sighted or heard Monal on more than 121 occasions. Khacher
(1978) did not see any Monal during his survey in 1977, though he
documented the presence of suitable habitats. Thus absolute protection has
certainly benefited this species.
5. Kalij Pheasant Lophura leucomelanos. Not seen during this survey, but is
present at Belta Kharak, and in forested areas around Lata and Reni village.
Its status there is unknown and some hunting pressure exists on this species.
6. Koklass Pheasant Pucrasia macrolopha. A rare bird within NDNP.
Occurred only in the forested area below Dibrugeta maidan. A single
sighting by me and one by the wildlife guards were the only two records of
this species during this survey. However, this bird was heard on at least 14
different occasions and the maximum number of individuals that I heard
was five. The feathers of a female pheasant found between Kalikona and
Chinwari were possibly of this species. Has the Koklass reduced in number?
Lamba (1987) recorded Koklass on 15 occasions with a total of 48
individuals. However, as he did not give the location of his sightings a
comparison cannot be made. Khacher (1978) heard them above Lata
village, an area I did not survey. Locals confirmed the continued presence
of the species in the area.
6. Cheer Pheasant Catreus wallichii. Not seen during this survey. This
pheasant occurs in the forested areas near Reni village and, like other
pheasants that occur near villages, appears to be under some hunting
pressure. Possibly one individual was heard at Belta Kharak (Negi, AWLW,
pers. comm.). It is unlikely that Cheer exist within NDNP, as they avoid
forested areas, but they are often found in association with agriculture
(Garson et al. 1992).
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Conservation
Total protection from all human use is a rarely implemented or achievable
conservation strategy in any of the protected areas of India. In the Himalaya,
biotic pressures like livestock grazing play a significant role in virtually all
temperate, subalpine and alpine areas during the summer months, with
deleterious effects on wildlife, particularly because optimal areas for livestock
grazing are also prime habitats for species like Himalayan Musk Deer,
Himalayan Blue Sheep Pseudois nayaur and the Himalayan Monal. In
addition to this are the often excessive pressures of adventure sports (e.g.
mountaineering and trekking), these having a negative impact, primarily
because of high levels of disturbance in areas abutting the trails. Thus
Nanda Devi National Park is of particular importance because, while it had
been extensively exploited in the past, there has been no, or minimal, human
interference in this area for the last 12 years.
This study, and the one on mammals (Sathyakumar 1993), has clearly
documented that absolute protection results in a significant increase in
mammal and bird abundance, particularly of the species that are easily
displaced because of disturbance. Based primarily on this major finding I
propose the following conservation strategies.
1) A continuation of the total ban on mountaineering or other expeditions
within the Nanda Devi National Park. To even allow limited exploitation
could result in a reversion of all that has been achieved in these last 1 2 years .
2) The buffer of NDBR is a multiple use area, where needs of nearby villages
are met, e.g. fuel and fodder. Several areas of the buffer zone are rich in fauna
(Rastogi 1993) and hunting and other disturbance to wildlife is apparently
widespread. Furthermore, there is probably excessive or unsustainable
collection of medicinal plants of commercial value. The need in NDBR is
not to waste valuable resources and personnel on the NDNP (which is in
excellent condition) but to increase personnel and patrolling in the wildlife
rich areas of the buffer zone and adjacent areas, and inculcate the principles
of sustainable exploitation of plants of economic value amongst the locals.
3) Almost all species of avifauna in the Himalaya show altitudinal migration,
ascending into subalpine and alpine areas in summer to breed, and descending
into temperate and tropical areas in the winter when snow and extreme
climatic conditions create a resource crunch at higher altitudes. The lower
temperate and tropical forests of the Himalaya are perhaps amongst the
most vulnerable in this biogeographic zone, simply because this is the
inhabited belt. It is in the lower temperate and tropical belt that maximum
deforestation is taking place (D. Mohan pers. comm.). Apparently, most
protected areas in the western Himalaya are situated at higher altitudes,
encompassing mostly alpine or subalpine areas. Do these protected areas
have sufficient temperate and tropical forest below them into which birds
can descend during winter? Careful consideration needs to be given to the
1994
Birds of Nanda Devi National Park, India
125
planning and establishment of a protected area network around and below
high altitude protected areas so as to ensure that the forested and other areas
at lower altitudes, which are used for wintering by birds, are adequately
protected. Lack of sufficient protection of wintering areas will result in
reduction in the populations that migrate into alpine or subalpine areas to
breed.
4) Despite the fact that, during this survey, the forests at Auli (above
Joshimath) were the least surveyed, species richness was the highest there.
I propose that a specific study is made to find ways and means by which to
better protect this excellent forest.
Thanks are due to several individuals whose help during and after the expedition helped me greatly.
In alphabetical order: Md. Ameen Naik, A. Baindur, B. Balodi, V. K. Bhatt, Ajith Kumar, Kundan
Singh, Y. P. S. Pangtey, A. Rastogi, S. S. Samanth, S. Sathyakumar, G. K. Sharma and Lalitha
Vijayan.
REFERENCES
Ali, S. and Ripley, S. D. (1983) Handbook of the birds of India and Pakistan. Compact edition. Bombay:
Oxford University Press.
Casebolt, G. (1979) Bird list. Pp. ? in M. D. Clarke, Nanda Devi - 1978 Seattle Garhwal Himalaya
expedition.
Garson, P.J., Young, L. and Kaul, R. (1992) Ecology and conservation of the Cheer Pheasant Catreus
wallichiv. studies in the wild and the progress of a reintroduction project. Biol. Conserv. 59: 25-35.
Gaston, A. J., Garson, P. J. and Hunter, M. L., Jr. (1981) Present distribution and status of pheasants
in Himachal Pradesh, western Himalayas. World Pheasant Assoc. Jour. 6: 10-30.
Halberg, K. and Petersen, I. (1984) Himalaya 1978-83. Observations of birds, mammals and some
reptiles. Unpublished.
Hajra, P. K. (1983) A contribution to the botany of Nanda Devi National Park. Howrah: Botanical
Survey of India.
Khacher, L. (1979) The Nanda Devi Sanctuary - 1977. J. Bombay Nat. Hist. Soc. 75: 868-887.
Khacher, L. (1983) Nanda Devi - a goddess desecrated. Sanctuary 3: 38-49.
Lamba, B. S. (1987) Status survey of fauna: Nanda Devi National Park (mammals and birds). Records
Zool. Surv. India. Misc. Publ. Occ. Pap. 103.
Rastogi, A. (1993) Conservation status of forests in the buffer zone. Pp. 44-53 in Corps of Engineers’
scientific and ecological expedition to Nanda Devi National Park. New Delhi: Corps of Engineers.
Reed, T. M. (1979) A contribution to the ornithology of the Rishi Ganga valley and the Nanda Devi
Sanctuary. J. Bombay Nat. Hist. Soc. 76: 275-282.
Sathyakumar, S. (1993) Status of mammals in Nanda Devi National Park. Pp. 5-15 in Corps of
Engineers’ scientific and ecological expedition to Nanda Devi National Park. New Delhi: Corps of
Engineers.
Tak, P. C. and Kumar, G. (1987) Wildlife ofNanda Devi National Park: an update. Indian J. Forestry
10: 184-190.
R. Sankaran, Salim Ali Centre for Ornithology and Natural History , Kalampalayam P.O., Coimbatore 641 010, Tamil
Nadu, India
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APPENDIX
ANNOTATED LIST OF THE BIRDS OF NANDA DEVI
NATIONAL PARK RECORDED IN 1993
(INCLUDING BIRDS SEEN AT JOSHIMATH AND AULI)
Species
Snow Partridge Lerwa lerwa
Himalayan Snowcock Tetraogallus himalayensis
(Black Francolin Francolinus francolinus
Koklass Pheasant Pucrasia macrolopha
Himalayan Monal Lophophorus impejanus
(Rufous-bellied Woodpecker Dendrocopos hyperythrus
(Himalayan Woodpecker Dendrocopos himalayensis
Woodpecker Picidae
(Great Barbet Megalaima virens
(Eurasian Hoopoe Upupa epops
Common Cuckoo Cuculus canorus
Himalayan Swiftlet Collocalia brevirostris ?
Fork-tailed Swift Apus pacificus
Grey Nightjar Caprimulgus indicus
(Rock Pigeon Columba livia
Hill Pigeon Columba rupestris
Snow Pigeon Columba leuconota
Speckled Wood-Pigeon Columba hodgsonii
Oriental Turtle-Dove Streptopelia orienialis
Lammergeier Gypaetus barbatus
Himalayan Griffon Gyps himalayensis
Eurasian Sparrow-hawk Accipiter nisus
Long-legged Buzzard Buteo rufinus
Golden Eagle Aquila chrysaetos
Booted Eagle Hieraaetus pennatus
Falcon Falco
Common Kestrel Falco tinnunculus
(Long-tailed Shrike Lanius schach
(Eurasian Jay Garrulus g/andarius
(Black-headed Jay Garrulus lanceolatus
(Blue Magpie Urocissa erythrorhyncha
(Grey Treepie Dendrocitta formosae
Spotted Nutcracker Nuci/raga caryocatactes
Red-billed Chough Pyrrhocorax pyrrhocorax
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Birds of Nanda Devi National Park, India
127
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Brownish-flanked Bush-Warbler Cetlia fortipes
Chestnut-crowned Bush-Warbler Ceuia major
Bush-Warbler Cettia sp.
Sulphur-bellied Warbler Phylloscopus griseolus
Pale-rumped Warbler Phylloscopus chloronotus
Greenish Warbler Phylloscopus trochiloides
Large-billed Leaf-Warbler Phylloscopus magnirostris
Western Crowned Warbler Phylloscopus occipitalis
Blyth’s Leaf-Warbler Phylloscopus reguloides
Golden-spectacled Warbler Seicercus burkii
Grey-hooded Warbler Seicercus xanthoschistos
Streaked Laughingthrush Garrulax lineatus
Variegated Laughingthrush Garrulax variegatus
Chestnut-tailed Minla Minla strigula
(Rufous Sibia Heterophasia capistrata
Yellow-bellied Flowerpecker Dicaeum melanoxamhum
(House Sparrow Passer domesticus
Grey Wagtail Motacilla cinerea
Olive-backed Pipit Anthus hodgsoni
Rosy Pipit Anthus roseatus
Alpine Accentor Prunella collaris
Robin Accentor Prunella rubeculoides
Rufous-breasted Accentor Prunella strophiata
(Fire-fronted Serin Serinus pusillus
Plain Mountain-Finch Leucosticte nemoricola
Common Rosefinch Carpodacus erythrinus
Beautiful Rosefinch Carpodacus pulcherrimus
Pink-browed Rosefinch Carpodacus rodochrous
Spot-winged Rosefinch Carpodacus rodopeplus
White-browed Rosefinch Carpodacus thura
Red-fronted Rosefinch Carpodacus puniceus
Red-headed Bullfinch Pyrrhula erythrocephala
(Black-and- yellow Grosbeak Mycerobas icterioides
Spot-winged Grosbeak Mycerobas melanozanthos
Belta Kharak,
Key :
Habitat
1 = Alpine meadow
2 = Subalpine forest
3 = Upper temperate forest
4 = Water courses/bodies
5 = Cliffs
6 = Boulder-strewn slopes with sparse vegetation
7 = Agriculture/habitation
Abundance ranking (based on sightings or calls heard)
1 = 1
2 = 2-5
3 = 6-10
4 = 11-50
5 = 50-100
6 = >100
( ) = indicates species seen only outside NDBR
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FORKTAIL 10 (1994) 129 -140
129
Occurrence of some pelagic seabirds
(Procellariiformes) in waters off the
Indian subcontinent
A. L. H. ROBERTSON
Information on the occurrence and movements of petrels Procellariiformes in the northern Indian
Ocean is summarised. An attempt is made to integrate these pelagic and migratory species from the
southern fringe of the Oriental region more firmly within the avifauna of the Indian subcontinent.
Some additions to the regional avifauna are noted.
Petrels, shearwaters and storm-petrels (Procellariidae) are truly pelagic
birds, often returning to land only to breed. Many species are also highly
migratory at sea, following ocean currents and upwellings in search of food
during the non-breeding season (Harrison 1985, Warham 1990). In the
Indian Ocean north of the equator there are few known breeding sites and
individuals are seldom examined in the hand. Information has been sparse
and scattered (Bailey and Bourne 1963, van den Berg et al. 1991) and the
recording of most species near the coasts of the Indian subcontinent is based
largely on sporadic sight records and in some cases specimens (Ripley 1982,
Ali and Ripley 1987), the latter usually washed ashore or caught by
fishermen.
A search of the literature on seabirds in the Indian Ocean, including the
published records of the Royal Naval Bird Watching Society, has revealed
much extra information on the occurrence and movements of these birds
relative to the subcontinent and its off-shore island groups. It is hoped that
summarizing these data, and providing a deliberately long list of references,
will help to stimulate further research.
Numbers in parentheses after the scientific name are those used in Ripley
(1982). Following the taxonomy of Sibley and Monroe (1990) all the
species treated fall within the Procellariidae and Persian Shearwater is
treated as a separate species. Nomenclature conforms with that preferred by
Bourne and Casement (1993).
NOTES ON SPECIES
Cape Petrel Daption capense (6)
A circumpolar species from the Southern Oceans, very occasionally straying
north.
130
A. L. H. ROBERTSON
Forktail 10
A single undated specimen collected prior to 1870 and said to have been
killed between Sri Lanka and the Indian mainland is in the Hume collection
at the British Museum (Tring) (R. Prys-Jones pers. comm., Whistler 1944).
It is one of only about a dozen records from north of the equator (Bourne
1967a) and the only specimen from the northern Indian Ocean. However,
Legge (1880) reported a second instance of its occurrence south of Sri
Lanka at about 03°N in November 1866 and there is a more recent sight
record off south-east Arabia (Landers 1957).
[Mascarene Petrel Pterodroma aterrima (13)
For many years known only from four 1 9 th century skins from the Mascarene
Islands; it has been recently collected on Reunion. Little is known of its
range and distribution (Harrison 1985) and Feare (1984) considers it ‘may
well be the rarest of tropical Indian Ocean seabirds’. Reports of its
occurrence in the Arabian Sea, such as those noted by Alexander (1954),
have been open to doubt since the discovery and naming of the similar¬
looking Jouanin’s Petrel Bulweria fallax in 1955, and in all probability refer
to the latter species (Jouanin 1970a).
Its only reported occurrence from the subcontinent was of a specimen
collected alive by fishermen near Bombay in June 1 940 and identified by G.
M. Henry at the Colombo Museum (Abdulali and Ali 1 940) . In light of the
subsequent discovery of B. fallax the specimen should be re-examined but
its whereabouts are unknown (Bailey and Bourne 1963, Ripley 1982) and,
even without it, there is doubt as to its identity (Jouanin 1970a).]
Barau’s Petrel Pterodroma baraui (— )
First described in 1963 and known only from the Indian Ocean where it
breeds on the Mascarene islands (Jouanin 1987).
Initially thought not to migrate north of the equator (Bailey 1968) it has
now been shown that it does disperse north-east of its breeding range. Four
sightings off the south-east coast of Sri Lanka (c. 05° 1 0’N 82°E) on 26 June
1 984 and two more in the 9° Channel between the Maldives and Lakshadweep
on 27 June 1985 were reported by the Dutch research ship Tyro (van den
Berg et al. 1991). Two sight records near Colombo in September 1991, a
single bird off Wellawatte (De Silva 1 992), and four birds off Mutwal on 8th,
have been reported (Warakagoda and Karunaratne 1993), and three other
sightings are listed by Warakagoda (1994), and one other in June by
Karunaratne et al. (1994).
The species is an addition to the recognised regional avifauna (Ripley
1982, Ali and Ripley 1987).
Soft-plumaged Petrel Pterodroma mollis ( — )
Primarily a bird of the Southern Oceans where it is most numerous between
25° and 60°S (Harrison 1985) and seldom appears in the northern
hemisphere.
1994
Occurrence of some pelagic seabirds off the Indian subcontinent
131
On 7 and 10 September 1988 landbased observers at Wellawatte beach,
Colombo (06°52 N 79°51’E) recorded a total of four separate sightings of
single birds, identified as this species by reference to the literature (De Silva
1989) . This is the first record of the species in the region and there have been
no further sightings (R. I. De Silva in litt. 1993, Warakagoda 1994).
In the Indian Ocean it is occasionally recorded north of the Tropic of
Capricorn, in June and July (Bourne 1966, Bourne and Radford 1961,
Bailey 1968), but there appear to be no other Indian Ocean records north
of the equator, so its appearance here needs to be confirmed.
Bulwer’s Petrel Bulweria bulwerii (13b)
Birds breeding in the East China Sea apparently disperse westwards in the
non-breeding season (Harrison 1985).
The first confirmed occurrence in the Indian Ocean was based on a single
specimen from Addu Atoll, Maldives (0°40’S 73°50’E) (Phillips 1959)
taken in August. It may have been an immature non-breeding bird summering
in the winter range (Bourne 1967a). Now known to regularly invade the
eastern edge of the Indian Ocean, travelling through Indonesian waters, and
commonly found off north-west Australia (Harrison 1985, Dunlop et al.
1988, Warham 1990), some birds at least penetrating further west.
One was sighted off Cape Comorin (07°11’N 76°17’E) on 20 August
1973 (Bourne 1984) and there have been sightings in the northern Indian
Ocean as far west as 51°42’E (Bailey et al. 1968).
Jouanin’s Petrel Bulweria fallax (13a)
The species was only named in 1955, having long been confused with
Puffinus pacificus or Pterodroma aterrima, and it is probably endemic to the
north-west Indian Ocean. Its breeding localities are still undiscovered and
it is conjectural whether they are in barren coastal ranges or on offshore
islands (Gallagher et al. 1984, Gallagher 1985, Warham 1990). It is found
commonly in the Arabian Sea, especially during the south-west monsoon,
dispersing south of the equator during the northern winter (Bourne 1987).
Roberts (1991) mentions possible sight records off Karachi and Sinclair
(1979) saw five birds west of the Gulf of Kutch on 25 November 1974.
A specimen was collected at Dehiwela near Colombo in January 1978
(Kotagama 1980). It has also been recorded at sea west of Lakshadweep
(11°24’N 70°48’E) on 1 October 1987 (Bourne 1989); south of Cape
Comorin (06°22’N 77°50’E) on 15 September 1986 (Chapman and
Cheshire 1987); south of Sri Lanka (05°29’N 81°22’E) on 24 June 1985;
west ofTrivandrum between 08°06’N 76°32’E and 08°22’N 75°42’E on 26
June 1985 (van den Berg et al. 1991); and in Lakshadweep in April 1988
(Daniels 1 992) . A probable record of the species in the vicinity of 1 0°N 72°E
is reported by Pocklington (1967), and off Colombo on 18 June 1994 by
(Karunaratne et al. 1994).
132
A. L. H. ROBERTSON
Forktail 10
Earlier records, of Pterodroma aterrima in particular, may refer to this
species (Jouanin 1957, 1970a) and it is now evident that it does indeed occur
in subcontinental waters.
Streaked Shearwater Calonectris leucomelas (7)
A Pacific Ocean species, breeding around Japan, that occasionally strays
through the Malacca Straits into the Indian Ocean (Harrison 1 985, Warham
1990).
Ripley (1982) lists only a single specimen from near Colombo, taken in
either 1884 or 1894, though Phillips (1967 and 1978) noted another British
Museum specimen taken in the Gulf of Mannar in December 1956.
More recently the species has been recorded at sea off the coasts of Sri
Lanka: in the east (08°N 82°30’E) on 5 October 1962 and between Gt.
Basses reef and Dondra Head (06°N 80°45’E) on 1 3 October 1 962 (Bourne
1965); in the south-west (06°06’N 79°09’E) four birds on 18 December
1979 (Chapman 1983); and in the Gulf of Mannar, observed from the ferry
between Talaimannar and Rameshwaram on 21 September 1978 (van den
Berg et al. 1982b). A bird was photographed off Cape Comorin (07°53’N
77°47’E) on 22 June 1984 (van den Berg et al. 1991).
Sri Lanka lies on the western edge of its normal range (W. R. P. Bourne
in litt. 1993) but it has reached as far as Eilat (Morgan and Shirihai 1992).
Wedge-tailed Shearwater Puffinus pacificus (9)
The Indian Ocean population breeds only in the warm water areas of the
Southern Hemisphere (Bailey 1968, Warham 1990) including the Chagos
Archipelago. After breeding in the southern summer colonies disperse
northwards to range widely throughout the tropical waters of the Indian
Ocean (Jouanin and Mougin 1979).
In the area between the the Maldives and Sri Lanka it is perhaps the
commonest shearwater during the northern summer, occurring between
March and October (Phillips 1954 and 1963, Bourne and Dixon 1975,
Bourne 1984, Wijesinghe 1985, Warakagoda 1994). It has been recorded
in May in Lakshadweep (Bailey 1968) and there is a report outside this
season from west of Goa (15°N 72°E) on 20 January 1984 (Chapman
1985). It was observed by van den Berg et al. (1991) to be a good deal
commoner east of the 81°E meridian.
Identification at sea is difficult and this species may be confused with the
next, while older sight records from the Arabian Sea may refer to Buhveria
fallax.
Flesh-footed Shearwater Puffinus cameipes (8)
A population migrates from its breeding range off western Australia north
across the equator to moult in the northern Indian Ocean (Bourne 1960),
where it is common during the months of the south-west monsoon,
numbers increasing from May to a peak in July-August and most birds
having departed by October (Bailey 1966).
1994
Occurrence of some pelagic seabirds off the Indian subcontinent
133
Records summarised by Abdulali and Grubh (1982) included two birds
purchased from fishermen at Kanyakumari [Cape Comorin] in May; sight
records from Addu Atoll in the Maldives in March, July and October; and
one in August about 400 km west of Minicoy, Maldives. They also noted the
statement by Bourne (1960) that numbers have been recorded off Cochin,
India in September on return passage. Some specimens are known from the
western coast of Sri Lanka. Four are in the Department of National
Museums, Colombo, including the first, which was collected in 1879, and
the fifth and sixth collected in 1944 and 1961 respectively. The seventh
specimen was blown ashore at Colombo in October 1991 (Gunawardana
1993).
To this list may be added: a single bird east of 9° Channel on 7 August
1951 (Norris 1952); several small flocks, mostly heading north-west or
west, seen west of Lakshadweep in May (Bailey 1968); numbers both east
and west of One and Half Degree Channel in the Maldives on 1-2 August
1980 (Chapman 1982); sightings along the length of the Maldives in late
April and off Goa (14°48' 73°41’E) on 3 May 1964 (Gill 1967); 28 birds off
Cochin (10°06’N 75°35’E) on 1 1 August 1987 (Bourne 1989); and a total
of 361 birds on five days in June 1984 and June 1985 between Cape
Comorin, Colombo and off the south-east coast of Sri Lanka (van den Berg
etal. 1991).
Sooty Shearwater Puffinus griseus ( — )
This widely distributed species has been shown to occur in the Red Sea from
mid-March to early August (Shirihai 1987) and a beached specimen was
recovered in Oman in July (Colston and Gallagher 1983). It is otherwise
unknown in the northern Indian Ocean, with the exception of the sight
record of birds off Trincomalee in November 1974 (Sinclair 1977, De Silva
1990). The identification in this instance was not in doubt but further
records would be desirable. An addition to the regional avifauna.
Short-tailed Shearwater Puffinus tenuirostris (10)
The species migrates in the Pacific between the Bass Straits and the
Aleutians, possibly in a vast figure-of-eight across the ocean (Warham
1990).
It has occurred twice in subcontinental waters, once in Pakistan in 1899
(Roberts 1991) and once in Sri Lanka in 1949 (Phillips 1951 and 1978).
Bourne (1967a) considered these ‘wrecked on the beach at the time of the
northward migration in May. A clear example of movement north from the
Southern Ocean into the wrong ocean’.
Two specimens were found in 1977, also in May, off western peninsular
Thailand (Frith 1978) but there appear to be no further records of the
species from the northern Indian Ocean other than that reported by
Karunaratne et al. (1994) in June off Colombo.
134
A. L. H. ROBERTSON
Forktail 10
Audubon’s Shearwater Puffinus Iherminieri (11)
Widely distributed through tropical seas with three possible subspecies
resident in the Indian Ocean - P. 1. bailloni , P. 1. nicolae and the recently
named P. 1. temptator. They are considered mainly sedentary (Bailey 1968,
Jouanin and Mougin 1979) though to some extent following ocean upwellings
(Bailey 1971).
Contra Ripley (1982) the race bailloni is now confined to birds breeding
in the Mascarenes (Jouanin 1970b, Louette and Herremans 1985) while
those breeding in the Maldives, certainly in December and January and
possibly throughout the year (Phillips and Sims 1958), and probably also in
Lakshadweep and Chagos (Bailey 1968), are considered to be nicolae. The
only record in the area away from breeding localities is of one seen in Sri
Lanka in 1982 (De Silva 1990).
Persian Shearwater Puffinus persicus (12)
Breeds in summer on the cliffs of the Kuria Muria islands off Arabia
(Gallagher 1985) and possibly elsewhere (Gallagher et al. 1984).
It can be regularly sighted off the Makran coast of Pakistan (Roberts
1991) and has strayed as far as Trivandrum (8°30’N) (Bourne 1960).
Wilson’s Storm-Petrel Oceanites oceanicus (14)
A notable migrant and abundant visitor to the northern Indian Ocean from
its breeding grounds in the Southern Ocean (Bailey 1971, Warham 1990)
and probably the most widespread storm-petrel in subcontinental waters
during the northern summer.
Large numbers are reported to be present from April to October in the
seas around the Maldives (Phillips 1963) and mass southerly migration has
been noted off Sri Lanka and south India (Phillips 1954 and 1955, Dawson
1958, Bourne and Dixon 1973 and 1975, van den Berg etal. 1982a). At the
Bombay High oilfields (19°37’N 71°23’E) it has been reported as the
commonest and most widespread offshore species in September (Chapman
1984). The record of six birds off the mouth of the Hugh river, West Bengal
(c. 21°30’N) on 1 1 May 1964 and one on 30 May 1965 are the most
northerly records in the Bay of Bengal (Bourne 1967b). Roberts (1984 and
1991) indicates that non-breeding birds may remain in the northern Indian
Ocean all year and can be observed along the coast of Pakistan.
White-faced Storm-Petrel Pelagodroma marina ( — )
Birds from the south-west Australian breeding population P. m. dulciae
migrate to the western Indian Ocean where they are quite common in the
northern summer from late May to September (Junge 1941, Bailey 1966
and 1968, Harrison 1985, Warham 1990). Migrating birds pass through
subcontinental waters, but the occurrence of the species was not noted by
Ripley (1982) or Ali and Ripley (1987).
A number of records exist relevant to the species’ passage including, listed
chronologically:
1994
Occurrence of some pelagic seabirds off the Indian subcontinent
135
specimen taken (AMNH)
“ “ (ZMA 17692)c
shipboard bird photographed
one on board ship
two observed
bird on board ship
four observed
bird on board ship
three birds on board ship
bird on board ship
two birds on board ship
dead bird ashore
one observed
one observed
Morzer Bruyns and Voous (1964)
« U
Bailey and Bourne (1963)
Junge (1941)
van den Berg et al. (1991)
Bourne and Radford (1961)
van den Berg et al. (1991)
Bourne (1966)
U U
(( K
Strickland and Jenner (1978)
Ash and Shafeeg (1994)
Voous (1965)
The species is relatively easily distinguished at sea from other storm-
petrels by its white face, almost entirely white underside, and pale grey
rump. It is clearly evident that it occurs in subcontinental waters, certainly
on its northward passage, passing direct from the breeding grounds to the
wintering area in the Arabian Sea (Bailey 1968), though the lack of records
in August-September indicates that it may return by a more southerly route.
Birds have been reported from the Chagos islands in July (Bourne 1971) and
in October (Bourne 1985).
Black-bellied Storm-Petrel Fregetta tropica ( 1 5)
White-bellied Storm-Petrel Fregetta grallaria ( — )
The genus Fregetta is taxonomically complex but usually divided into two
species, each with two colour phases often difficult to identify in the field
with certainty. They breed in the Southern Oceans, migrating north to the
tropics (Jouanin and Mougin 1979) and are common in the Arabian Sea
from May to September (Bailey 1968 and 1971). Specific identification of
birds observed at sea is often open to doubt.
For many years the only record of F. tropica in the region was of a specimen
from the ‘Bay of Bengal’ in the British Museum (Gibson-Hill 1948, Ripley
1982). The date of circa 1895 given for this specimen by Ali and Ripley
(1987) must be wrong since the label is apparently in the handwriting of the
ninth Marquis of Tweeddale who died in 1878.
An example of F. tropica caught at 08°03’N 72°50’E - off Minicoy in the
8° channel - on 9 September 1960 was considered the first which has
actually been handled in recent times in the Indian Ocean north of the
equator (Bailey and Bourne 1963). The only positive records since are of
three seen west of 9° Channel (c. 08°48’N 70°17’E) on 20 June 1984 and
two more south-east of Sri Lanka (c. 04°52’N 82°40’E) six days later (van
den Berg et al. 1991).
Abdulali (1981) noted a sight record on 12 April 1977 off Battye Malve,
south of Car Nicobar, which ‘may have been of this species’, while Cheke
(1966) recorded a Fregetta sp. in the Bay of Bengal (05°56’N 87°E) on 7
136
A. L. H. ROBERTSON
Forktail 10
August 1963, and Bourne and Dixon (1973) refer to two Fregetta seen at
12°15’N 74°E on 27 July 1967.
Birds that may have been F. grallaria were observed off Lakshadweep
(12°21’N 74°05’E) and 250 miles west of Goa (15°04’N 70°56’E) (Anon.
1970) but the only confirmed record in subcontinental waters is of a bird
seen in the 1° Channel in the Maldives (01°30’N 73°30’E) by R. C.
Anderson in August 1994 (Ash and Shafeeg 1994).
Swinhoe’s Storm-Petrel Oceanodroma monorhis (16)
Breeds around the Sea of Japan and migrates westwards to the Indian
Ocean, with stray birds reaching as far as the Arabian and Red Seas, but their
movement in the Indian Ocean is very inadequately documented (Warham
1990).
Bailey et al. (1968) summarised records from the Indian Ocean up to that
time, of which they considered only two as definite, including one found
exhausted on the shore in Sri Lanka on 3 July 1927 (Gibson-Hill 1953).
They also noted a number of possible records, including one from Port
Blair, Andamans. In the course of their study they collected two further
specimens in the Arabian Sea, plus additional sight records in subcontinental
There is also a record of a bird caught and banded in Lakshadweep
(11°40’N 72°25’E) on 20 October 1963 (Mathew and Ambedkar 1964).
Mohan (1989) recorded small numbers off the coasts of several islands in
Lakshadweep in early 1987. Some tentatively identified sightings are
reported by van den Berg et al. (1991), and De Silva (1990) mentions one
collected at Colombo harbour in 1 97 5, and other sightings off Colombo in
June have recently been reported (Karunaratne et al. 1994)..
It has sometimes been considered a race of O. leucorhoa (Ali and Ripley
1987, De Silva 1990, Ripley 1982, Simpson 1990) and possible confusion
in the literature may be compounded by the discovery that stragglers of the
nominate race of O. leucorhoa have occurred in the western Indian Ocean
(Lapthorn et al. 1970).
[Matsudaira’s Storm-Petrel Oceanodroma matsudairae ( — )
A highly migratory species, moving from its confined breeding area south
of Japan into the western equatorial Indian Ocean where it is most common
between June and September (Bailey et al. 1968). Their exact migration
route is unknown but it is possible that the species may be found, as a
passage migrant, in the southern Maldives, probably within 5° of the
equator.
1994
Occurrence of some pelagic seabirds off the Indian subcontinent
137
Two possible sight records exists in the region: of a bird at 01°N 78°E on
25 July 1964 (Bourne 1966), and of five in the wake of a ship at 01°27’N
80°E on 18 November 1984 (Chapman 1986).]
DISCUSSION
The tendency of some Procellariiformes to long distance wandering into
strange waters, their often difficult identification, plus less than perfect
viewing conditions found on board ship combine to give a degree of
uncertainty to many sight records. However, present evidence would
indicate that more species may occur more regularly, particularly around
the time of the south-west monsoon, than have traditionally been thought
to reach subcontinental waters.
Our knowledge of the seabirds of the Indian Ocean remains patchy,
though there has been some advance since the situation was reviewed twenty
years ago by Bourne (1974). Such areas as the Bay of Bengal offer rich
opportunities for research. The likelihood that other species not listed here
will be found to occur is strong. An unusual petrel sighted west of Cape
Comorin, India was thought to be either Atlantic Petrel Pterodroma incerta
or Tahiti Petrel P. rostrata (van den Berg etal. 1991), most likely the former
(Bourne 1992), and White-headed Petrel Pterodroma lessoni has been
tentatively identified off Colombo in September 1990 (De Silva 1992 and
inlitt. 1993).
I wish to thank Dr W. R. P. Bourne and T. Inskipp for their invaluable comments on the manuscript
and for pointing out a number of important references in the literature, and R. I. de Silva for clarifying
recent information on Sri Lankan records. My thanks also to Dr R. Prys-Jones for his speedy and full
response concerning specimens held at Tring.
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1994
FORKTAIL 10 (1994): 141 - 158
141
A new subspecies of Spectacled Fulvetta
Alcippe ruficapilla from Vietnam
JONATHAN C. EAMES, CRAIG R. ROBSON and NGUYEN CU
A new subspecies of Spectacled Fulvetta Alcippe ruficapilla [Timaliini (Timaliidae)], believed to be
endemic to the Da Lat Plateau in southern Vietnam is described. It is restricted to upper montane
forest above 2,100 m elevation. The most distinctive characters are its general dullness and the
absence of whitish-grey and blackish on the outer webs of the primaries.
INTRODUCTION
On 22 May 1991 the authors, together with Truong Van La, observed an
unfamiliar fulvetta Alcippe , thought to belong to the group of species
comprising Streak-throated A. cinereiceps and Spectacled A. ruficapilla. It
was at 2, 1 60 m elevation on Nui Bi Doup in Lam Dong Province, southern
Vietnam. On 23 May this individual was again observed and later, a flock
of at least four was seen on the summit at 2,289 m. One of the four
individuals observed on the summit was mist-netted, and a series of
biometrics was taken before it was released (Robson et al. 1993).
On 12 December 1993 whilst on a return visit, J.C.E. and N.C. observed
six birds of the same form, on the summit of Nui Bi Doup, and on 13
December trapped nine individuals, of which a series of seven specimens
was collected.
On 16 January 1994, above 2,200 m on Chu Yang Sin in neighbouring
Dac Lac Province, J.C.E. observed three flocks of the same Alcippe ,
consisting of five, eight and three birds respectively. On 1 7 January, J.C.E.
trapped and photographed two birds, on 26 January J.C.E. and N.C.
observed and trapped a flock of six birds at 2,210 m, and took a series of
biometrics before all the birds were released. The species was common
along the summit ridge on 27 January and recorded commonly at the
summit (2,442 m).
FORMAL DESCRIPTION
The birds seen and collected on Nui Bi Doup in 1991 and 1993, and
observed on Chu Yang Sin in 1 994 are of a previously undescribed taxon for
which we propose the name
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J. C. EAMES, C. R. ROBSON and NGUYEN CU
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Alcippe ruficapilla bidoupensis ssp. nov.
Holotype
Institute for Ecology and Biological Resources, Hanoi, number BT 2341,
adult female collected on Nui Bi Doup, Lam Dong Province, Vietnam ( 1 2°
05’N 108° 40’E), on 13 December 1993. Collectors J.C.E. and N.C.
(Figure 1).
Diagnosis
A small, arboreal, flocking babbler assigned to Alcippe due to the presence
of a short, only slightly decurved culmen; short-rounded wings; soft
plumage; lateral crown-stripes and an eye-ring. Plumage brown above and
vinous buff and rufescent-brown below. The remiges are brown and have
no blackish or whitish-grey edgings on the outer webs of the primaries
(Figures 2 and 3).
Description of holotype
Forehead and crown greyish-brown with an olive tint. Narrow white
supercilium extending from the lores to behind the eye, where it becomes
duller and buff-tinged; it also extends more narrowly over the base of the bill
but is buffy and less conspicuous there. Lateral crown-stripes blackish-
brown extending and broadening from above eye to nape. Whitish eye-ring,
broken by inconspicuous grey eye-stripe. Ear-coverts and cheeks vinous-
pink or vinous-buff, lightly streaked with brown. Mantle, scapulars and
upper wing-coverts, warm rufescent brown. Rump slightly more rufous
than mantle. Chin and throat whitish becoming pale vinous-buff on upper
breast, distinctly paler than ear-coverts. Streaking on throat and upper
breast formed by brown shaft-streaks on feathers. Streaking becomes more
distinct on upper breast. Belly whitish-buff, similar to throat, grading to
ochre-buff or orange-buff on the vent and undertail-coverts. Flanks vinous-
buff. Outer webs of remiges rufescent brown, intermediate in colour
between mantle and rump. Rectrices dull blackish-brown on inner webs
and rather more rufous-brown on outer webs. The bill of the freshly dead
bird was flesh-horn, slightly paler at the tip and along the cutting edge. By
July 1994 the upper and lower mandibles had become entirely dark-horn,
except for a flesh base to the lower mandible. Tarsus and toes dark horn,
the soles paler. Iris dark brown. Full biometrics are given in Table 1.
Paratypes
Six paratypes are designated, all collected by J.C.E. and N.C. at the same
1994
A new subspecies of Spectacled Fulvetta from Viet Nam
143
locality and on the same date as the holotype. Five of the paratypes are held
at the Institute of Ecology and Biological Resources, Hanoi, the sixth is held
at the Museum of Natural History, Tring, U.K.
Individual variation
Variation in soft part coloration and biometrics between the seven type
specimens and six other individuals for which data are available are
presented in Table 1. All of the 13 birds were believed to be adults.
Although the sample of sexed individuals was small (n = 7), the available
data indicate that males, on average, have a longer tarsus, wing and tail and
are heavier than females.
RELATIONSHIPS AND RECOGNITION
Within the genus Alcippe, the species vinipectus, striaticollis , ruficapilla,
cinereiceps and ludlowi are similar in size and general appearance, with
brownish upperparts and a distinct pale flash or panel on the wing formed
by pale grey or whitish on the outer webs of the primaries. Taxa assigned
to A. ruficapilla are generally typified by having a brown, not black, bill; a
dark iris; vinous-brown ear-coverts, throat and upper breast; and a distinct
whitish eye-ring. The taxa assigned to A. cinereiceps, are typified by a black
bill (except A. c. formosana ); a pale iris; greyish to greyish-brown ear-coverts,
throat and breast; and the absence of white around the eye and on the
supercilium (except A. c. formosana). The morphological variation within
the two species is summarised in Tables 2 and 3.
The other three species in the group differ in a number of features. A.
vinipectus has a broad white supercilium bordered above by a dark lateral
crown-stripe; dark ear-coverts; and whitish throat and upper breast (marked
with brown to warm brown streaks in some races). A. striaticollis has no
obvious supercilium; dark brown lateral crown-stripes; faint dark brown
streaks on forehead and crown; huffish tinged mid-brown ear-coverts and
pale underparts with conspicuous dark greyish-brown streaks on the throat
and upper breast. A. ludlowi has head (apart from throat) warm mid to dark
brown; no supercilium; dark lateral crown-stripes almost obsolete; throat
and upper breast white with broad, warm dark brown streaks. A. ludlowi was
treated as conspecific with A. cinereiceps by Deignan (1964), apparently
following Delacour (1946), although neither author gave any reasons for
their treatment. However, in view of its very distinct morphological and
biometrical characters treatment as a separate species is warranted.
Additionally, it was recently found in the same locality as A. c. manipurensis
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J. C. EAMES, C. R. ROBSON and NGUYEN CU
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Table 1. Biometrics of Alcippe ruficapilla bidoupensis (all measurements by J.C.E.)
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A new subspecies of Spectacled Fulvetta from Viet Nam
145
Figure 1 Alcippe ruficapilla bidoupensis
Hololype (photo. J. C. Earnes).
Figure 2 A. r. bidoupensis Nui Bi Doup 23
May 1991 (photo. J. C. Eames).
Figure 3 A. r. bidoupensis showing head in
detail, Chu Yang Sin 1 7 January 1 994
(photo. J. C. Eames).
Figure 4 Upper montane forest formation on
Chu Yang Sin, a transition zone between
Oak-laurel and Montane ericaceous vegetation
and the habitat of A. r. bidoupensis (photo.
J. C. Eames).
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J. C. EAMES, C. R. ROBSON and NGUYEN CU
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Table 2. Morphological differences exhibited within Alcippe ruficapilla and A. cinereiceps.
1994
A new subspecies of Spectacled Fulvetta from Viet Nam
147
Table 3. Bare parts and morphometric differences exhibited within Alcippe ruficapilla and A. cinereiceps
(all measurements, except those for A. r. bidoupensis by C.R.R.)
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J. C. EAMES, C. R. ROBSON and NGUYEN CU
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Figure 5 Localities mentioned in text
in eastern Arunachal Pradesh, India in March, at which time some
neighbouring populations of the latter are in breeding condition.
Bidoupensis exhibits characters generally ascribed to taxa in the A.
ruficapilla group. However, the wing panel conspicuously shown by all the
taxa currently assigned to the above-mentioned species, is absent in bidoupensis
and much reduced in A. r. danisi. The darker brown bill of bidoupensis and
danisi and the greyish-brown tones in the crown of both taxa place them
closely together and slightly removed from A. r. ruficapilla and A. r. sordidior.
The absence of a wing panel in bidoupensis suggests a cline within A.
1994
A new subspecies of Spectacled Fulvetta from Viet Nam
149
ruficapilla, of increasing dullness from north to south. Another scenario
should however, be briefly mentioned: it is arguable that bidoupensis and
danisi are sufficiently distinct from ruficapilla and sordidior to be lumped
together as a separate species, or as two separate species in their own right,
since they are arguably allospecies within a superspecies. For the time
being, however, we place bidoupensis within A. ruficapilla.
An additional point that is relevant here is that A. r. danisi is only known
for certain from Laos (see Appendix). However, Cheng (1987) listed it for
south-east Yunnan and south-west Guizhou, China, noting that they were
‘originally identified as A. r. sordidior , but from zoogeographical viewpoint,
the specimens collected probably belong to A. r. danisi. The identification
of these specimens remains doubtful (and they are treated separately in the
Appendix), especially since the measurements given for the specimens from
Guizhou (Wu et al. 1986) suggest a smaller bird than danisi and fit within
the range known for sordidior.
The scattergram shown in Figure 7 plots tarsus and wing lengths for four
subspecies of A. ruficapilla and six subspecies of A. cinereiceps ; where A. r.
ruficapilla n = 5, A. r. sordidior n = 18, A. r. bidoupensis n = 13, A. r. danisi
n = 1 ; and A. c. cinereiceps n = 3, A. c. fessa n = 2, A. c. fucata n = 3, A. c.
guttaticollis n = 17, A. c. manipurensis n = 14, A. c. formosana n = 7. Most
of the specimens were measured by C.R.R. in the collection of the Museum
ofNatural History, Tring; those of bidoupensis were measured by J.C.E., and
the specimen of danisi was measured by R. A. Paynter, Jr. at the Museum
of Comparative Zoology. The only specimen of A. c. tonkinensis in the
collection at Tring had a broken tarsus and this taxon is therefore omitted
from the figure. With reference to Figure 7, there is no clear pattern or
geographical dine; A ruficapilla shows the expected decrease in size from
north to south in China, but bidoupensis is bigger than both of the northern
subspecies.
ETYMOLOGY
We name this subspecies after Nui Bi Doup, the mountain on which the
holotype was collected. Mount (Nui) Bi Doup (2,289 m) is the second
highest mountain in the southern part of the western highlands of Vietnam.
The general area, known as the Da Lat Plateau and sometimes Langbian
(Langvien or Langbiang) Plateau, is noted for its high levels of endemism
in birds and plants (Eames and Nguyen Cu 1994). Of the four species of
bird endemic to this area, one bears the name Langbian, the Grey-crowned
Crocias Crocias langbianis. Some other endemic subspecies variously bear
the name annamensis derived from the old provincial name Annam, or
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J. C. EAMES, C. R. ROBSON and NGUYEN CU
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Figure 6 Distributional ranges of related taxa mentioned in text
1994
A new subspecies of Spectacled Fulvetta from Viet Nam
151
Figure 7 Scattergram showing correlation between tarsus and wing length of five subspecies of A.
ruficapilla and A. cinereiceps.
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J. C. EAMES, C. R. ROBSON and NGUYEN CU
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dalatensis after Da Lat, the largest city in the area. The plant Elaeocarpus
bidoupensis (Elaeocarpaceae) is similarly named after Nui Bi Doup.
It is hoped that by naming the taxon bidoupensis attention will be drawn
to the need for full establishment of the Thuong Da Nhim and Chu Yang
Sin Nature Reserves in which Nui Bi Doup and Chu Yang Sin are located.
BEHAVIOUR
The first individual observed on Nui Bi Doup in 1991 appeared, by its
behaviour, to be defending a territory in bamboo undergrowth along a
narrow ridge. The bird persistently called from the undergrowth and was
quite confiding. It showed a strong response to play-back of its alarm call.
Other birds of this taxon observed at this time were however, in a small flock.
In January on Chu Yang Sin birds were only ever observed in flocks and
were not territorial. The species was only observed in single species flocks.
VOCALIZATIONS
The alarm call is high-pitched and rapid, and consists of a number of similar
notes and phrases which could be transcribed as ‘ . .chuttachuttachuttachutta... . ’ .
The call is not loud but is constantly given by birds, especially when
mobbing a human at close quarters. What was believed to be the song of this
taxon was heard briefly on one occasion by C.R.R., and consisted of four
thin high-pitched notes, roughly transcribed as ‘ see-sew-see-see’ . Unfortunately
the singing bird was not seen to confirm the identification.
DISTRIBUTION
A. r. bidoupensis is currently only known from Nui Bi Doup, Lam Dong
Province and Chu Y ang Sin, Dac Lac Province, Vietnam. On Chu Y ang Sin
it is probably the commonest bird in the upper montane forest. The
subspecies is unlikely to be an altitudinal migrant as it was recorded at the
summit of Chu Yang Sin during the winter (Figure 4).
HABITAT
Floristically the habitat of A. r. bidoupensis could be described as being
within the transition zone between Oak-laurel and Montane ericaceous
forest (Whitmore 1990). On Nui Bi Doup A. r. bidoupensis was found in
1994
A new subspecies of Spectacled Fulvetta from Viet Nam
153
bamboo and undergrowth in broadleaved evergreen forest and in secondary
scrub in cleared areas. On the summit of Nui Bi Doup forest canopy height
varied from 4 to 10 m; canopy cover varied from 25% to 90% and ground
cover varied from 40% to 85%. A sample of 20 trees selected on the summit
comprised genera of the following families: Annonaceae (35%), Fagaceae
(40%), Lauraceae (10%), Myrsinaceae (10%) and Symplocaceae (5%).
On Chu Yang Sin the fulvetta was found in forest undergrowth, and also
in the forest canopy between 2,1 10 m and the summit at 2,442 m elevation
(Figure 4). Between these elevations canopy height varied from 3 to 1 5 m;
canopy cover varied from 40% to 95% and ground cover varied from 10%
to 95%. In a sample of 120 trees with a diameter at breast height (DBH)
of greater than 10 cm, within this altitudinal range, the following families
were recorded: Cupressaceae (2.5%), Ericaceae (34. 1%), Fagaceae (35.8%),
Hamamelidaceae (2.5%), Lauraceae (8.3%), Pinaceae (1.6%),
Podocarpaceae (1.6%), Theaceae (12%), unidentified (1.6%).
At around 2,000 m elevation on the north-facing slope of Chu Yang Sin
there is a rapid change in the forest structure. The trees become gnarled,
and lichen and moss-covered. In the undergrowth the bamboo A rundinella
setosa was common. Whilst the floral composition on the summit of Nui Bi
Doup was similar, its structure and appearance was quite different. This is
accounted for in part by the small extent of habitat on the summit of Nui Bi
Doup, and that part of the forest here has been felled by humans.
The fieldwork undertaken in 1991, by J. C. E., C. R. R. andN. C. was sponsored by the International
Council for Bird Preservation (now BirdLife International). The fieldwork undertaken by J. C. E.
and N. C. during 1993 and 1994, was undertaken whilst J. C. E. was an employee of BirdLife
International and N. C. an employee of the Institute for Ecology and Biological Resources, both on
secondment to WWF - The World Wide Fund for Nature Vietnam Programme as Project Executant
and Project Officer respectively, for WWF Project VN0008 - Development of a Protected Area
System. We would also like to acknowledge the Forest Protection Department of the Ministry of
Forestry (Hanoi) and the Provincial Forest Protection Departments of Lam Dong and Dak Lak for
facilitating this work. We would like to thank our colleagues, Truong Van La, Hoang Ngoc Long,
Nguyen Duy Chinh, Nong Van Tiep, Dinh Van Ty, Nguyen Va Qui, Tran Hong Chut and Ngoc
Quang Qui for their hard work and good company during fieldwork.
We would also like to acknowledge the assistance provided by Raymond A. Paynter, Jr. and the
Museum of Comparative Zoology, the Agassiz Museum, Harvard University and the Museum of
Natural History, Tring for providing access to specimens.
Finally we would like to thank Shanthini Dawson, Dr Rene Dekker, Tim Inskipp, Paul Jepson and
Uthai Treesucon for their many useful comments and suggestions and Mike Crosby for preparing the
map.
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156
J. C. EAMES, C. R. ROBSON and NGUYEN CU
Forktail 10
APPENDIX
Localities of subspecies of Alcippe ruficapillalcinereiceps
A. r. ruficapilla (Verreaux 1870)
China Gansu: sw + se (Cheng 1 987), Si-gu (= Siku 33°56’N 1 04° 1 8’E) + Huy-sian (?) (C. R. R. from BM
specimen labels)
Shaanxi: Qinling Mt. (Yao & Zheng 1986) = Zhouzhi 34°10’N 108°05’E and Liuba 33°35’E
106°58’E (Zheng et al. 1973)
Sichuan: Wanyuan 29°21’E 102°41’E (Cheng 1987), Baoxing 30°22’E 102°49’E (Li et al. 1976),
Guanxian 31°00’N 103°37’E (Cheng 1987), Emei 29°31’N 103°20’E (Zheng et al. 1963),
Chengkou 3 1 °57’N 1 08°40’E + Wanyan 32°05’N 1 08°03’E + Nanjiang 32°23’N 1 06°56’E (Yu
et al. 1986), Tangjiahe Natural Reserve 32°35’N 104°45’E (SFB/WWF PT 1986), Jiuzhaigou
33°08’N 103°55’E (Clements 1989), Tankwan, upper Minho (?) (Stresemann 1923)
A. r. sordidior (Rippon 1903)
China Sichuan: Huidong 26°39’N 102°35’E (Cheng 1987), Muli Mts. 27°56’N 101°17’E (Riley 1932);
Baurong 28°41’N 103°13’E + Yutza (?) (Bangs 1932, Stone 1933)
Guizhou: Weining (Cheng 1987) = Cao Hai 26°51’N 104°17’E, Guanfenghai 27°00’N 103°53’E,
Chengguan ?, Songmukan 26°43’N 104°10’E (Wu et al. 1986)
Yunnan: Lijiang 26°54’N 100°15’E, Shuangbai 24°42’N 101°39’E, Kunming 25°02’N 102°43’E
(Cheng 1987); Tengyueh 25°02’N 98°30’E (Rothschild 1921); Yunnanfu 25°03’N 102°43’E
+ Kopaotsun 24°58’N 103°00’E (La Touche 1923); Hofuping Mts. 28°10’N 98°55’E (Riley
1926); Yulo 27°10’N 100°03’E + Ndamucho ? (Riley 1932); Mt. Satseto, Lijiang Range
27°06’N 100°1 3’E (Greenway 1933); Tsangshan in Tali = Dali 25°42’N 100°09’E + Siaotsun
? + Waishan 25°14’N 100°18’E in Menghwa + Lichang = Lijiang 26°58’N 100°16’E in
Kiangchwan (Chong 1937); Mt. Yulung 27°08’N 100°13’E (Tan & Cheng 1964); Xujiaba
24°32’N 101o01’E - ssp not stated but presumably this (Wang and Wei 1983); Long Peng
23°53’N 1 02°33’E (Zheng 1 988); Yangtse Big Bend (?), Gyi-dzin-Shan, east of Talifu 25°50’N
100°18’E, Shayang-Chutung road 25°24’N 99°27’E, Meechu (probably = Mi-tu or Midu
25°14’N 100°18’E, T’ong-shan (?) (Rothschild 1926); Ao-wah ? (Bangs 1932), Mekong/
Salween divide 28°00’N 98°50’E + Yangtse valley 27°20’N 99°38’E + NW flank Lichiang range
27°30’N 100°15’E (C. R. R. from BM specimen labels)
A. r. danisi Delacour & Greenway 1941
Laos Phu Kobo 19°12’N 103°28’E (Delacour & Greenway 1941), Phou Bia 18°59’N 103°09’E (David-
Beaulieu 1 944); Nakay/Namtheun NBCA 18°07’N 105°23’E (R. Timmins and T. Evans in litt.
1994)
?A. r. danisi
China Yunnan: se (Cheng 1987) plotted at 23°10’N 104°20’E
Guizhou: Xingyi + Xingren (Cheng 1987) = Sandaogou c. 25°26’N 105°10’E, Laochang 25°41’N
104°56’E, Huopu 25°43’N 104°29’E (Wu et al. 1986)
A. c. cinereiceps (Verreaux 1870)
China Sichuan: Wanyuan 29°21’N 102°41’E, Emei 29°31’N 103°20’E, Baoxing 30°22’E 102°49’E,
Kangding 30°03’N 101°58’E (Cheng 1987), Chengwei c. 31°34’E 103°15’E + Cheng Gou
forks (Birckhead 1937, Stone 1933), Makaling (?) + Tachino (?) + Washan 29°21’N 103°02’E
(Thayer & Bangs 1912); Wolong 31°00’N 103°10’E (Clements 1989); Maowen 31041’E
103°51’E, Chengkou 31°57’N 108°40’E + Wanyan 32°05’N 108°03’E + Nanjiang 32°23’N
106°56’E (Yu et al. 1986), Pingshan County 28°4rN 104°03’E (Huang et al. 1993), Dayi
County 30°33’N 103o07’E (Zhang et al. 1994), Laba He Nature Reserve 30°13'N 102°25’E,
Tianquan County (Li et al. 1994); Dafcngding 28°50'N 103°10’E (King 1989), Gung Tang
Goh (?) (Traylor 1967), Kwanhsicn 31°00’N 103°37’E + Hwanglungze ncarSungpan (Sungpan
32°39’N 103°36’E + Wassuberge (?) (Stresemann 1923)
1994
A new subspecies of Spectacled Fulvetta from Viet Nam
157
Guizhou: Weining (Cheng 1 987) = Liangshan 26°52’N 1 04°05’E, Songmukan 26°43’N 1 04°1 0’E
(Wu etal. 1986)
3 unnan: Yanjin = Yanjian 28°05’N 104°1 5’E (Cheng 1987), Lishan in Yenting = Yanjian (Chong
1937)
A. c. fessa (Bangs & Peters 1928)
China Gansu: Lanzhou 36°05’N 103°40’E (Cheng 1987); Choni in Tao R. basin 34°35’N 103°30’E,
Wantsang Ku valley in Ha Tebbuland 33°56’N 103°37’E, Pezlu on the banks of Chuhungapu
in upper Tebbuland (?) (Bangs & Peters 1928)
Shaanxi: south (Cheng 1987), Tsinling Range, Taibai Shan, Qinling Mt. (Yao 1986) = Taibai
33°57’N 107°45’E and Zhouzhi 34°10’N 108°05’E (Zheng et al. 1973)
Ningxia: Liupan Mt. = Liupan Shan 35°40’N 106°12’E (Cheng 1987)
Sichuan: Jiuzhaigou 33°08’N 103°55’E (C. R. R. pers. obs.), Tangjiahe Natural Reserve 32°35’N
104°45’E - this or nominate, not stated (SFB/WWF PT 1986)
A. c. fucata (Styan 1899) (including berliozi Yen 1932)
China Guizhou: Suiyang (Cheng 1987) = Kuankuoshui 28°14’N 106°58’E (Wu et al. 1986)
Hubei: Hejiaping in Yichang (Cheng 1987); Hsien-shansien = PXingshan 31°14’N 110°46’E +
Ichang = Yichang 30°32’N 1 1 1°17’E + Hochaping (Greenway 1933, Thayer & Bangs 1912)
Hunan: south (Cheng 1987) plotted at 26°00’N 113°00’E, Ching-tung-schan (?) (Yen 1932)
A. c. guttaiicollis (La Touche 1897)
China Fujian: Guadun = Kuatun 27°45’N 117°35’E (Cheng 1987)
Guangdong: north (Cheng 1987) plotted at 24°00’N 114°00’E, Mahn-tsi-shan (?) (Mell 1922)
A. c. manipurensis (Ogilvie-Grant 1906) (including yunnanensis Rothschild 1922, insperata Riley 1930, menghzvaensis
Chong 1937)
Arunachal Pradesh: Ridgetop Camp 27°22’N 96°57’E (Ripley et al. 1991)
Assam: Barail Range (Ripley 1982) plotted at 25°20’N 93°25’E
Manipur: Owenkulno Peak = Twinkulno (?) (Ogilvie-Grant 1906)
Nagaland: Aichisagomi (?) (Stanford & Mayr 1941), Japvo 25°36’N 94°04’E + Zephu 25°38’N
94°46’E (Ripley 1952)
Yunnan: w + nw ranges between Lancang & Jinsha R., and those between Lancang & Nujiang R.
(Cheng 1987), Ndamucho (?) (Riley 1930), Tao-mung-chung 27°10’N 99°25’E and Chou-yu-
gko nearby (Greenway 1933), Gongshan area 27°44’N 98041’E (BSKIZAS 1980), Salween
valley 25°20’N 98°53’E + Peh Tu P’u, Yungping (Yungping 25°28’N 99°32’E) (C. R. R. from
BM specimen labels)
Kambaiti 25°25’N 98°07’E (Stanford 1935, Stanford & Ticehurst 1935)
Lungrebum 24°50’N 97°45’E (Stanford & Ticehurst 1938)
Htawgaw 25°56’N 98°22’E (Smythies 1949)
Pawahku 26°11’N 98°40’E (Smythies 1949)
?Chin Hills (Stanford & Mayr 1941)
A. c. tonkinensis Delacour & Jabouille 1930
Vietnam Fansipan 22°1 8’N 1 03°47’E
China Yunnan: Dawei Mt. 22°54’N 103°42’E (Zheng 1988), Xujiaba 24°32’N 101°01’E manipurensis/
tonkinensis (Wang & Wei 1983)
A. c. formosana (Ogilvie-Grant 1906)
Taiwan plotted at 23°30’N 120°45’E
A. ludlowi (Kinnear 1935)
Bhutan: Sakden 27°25’N 91°50’E, Dib La 27°35’N 91°40’E (on the border with India, Ludlow collected
on the Bhutan side), Yonpu La 27°15’N 91°30’E
China Xizang: sw Qamdo region (Cheng 1987), Tongyuk 29°58’N 94°48’E, Gyadzong 30°11’N
95°04’E, Showa 29°55’N 95°24’E, Nyuksang 29°46’N 95°00’E, Gyala 29°42’N 94°55’E
(Ludlow 1951), Dongjug 29°58’N 94°48’E, Tangmai 30°06’N 95°07’E (Robson 1986)
Arunachal Pradesh: Tawang 27°35’N 91°52’E (Ali & Ripley 1987), Ridgetop Camp 27°22’N
96°57’E (Ripley et al. 1991), Thingbu c. 27°40’N 92°20’E, Chakoo 27°05’N 92°30’E, Talley
Valley 27°40’N 93°48’E, Majha c. 28°20’N 93°55’E, Mayodia 28°14’N 95°55’E (Singh)
India
China
Myanmar
India
158
Forktail 10
1994
FORKTAIL 10 (1994): 159 - 172
159
A reappraisal of the taxonomy of the
Spotted Bush-Warbler
Bradypterus thoracicus
PHILIP D. ROUND and V. LOSKOT
Evidence is presented to suggest that the taxon Bradypterus thoracicus shanensis, which is known only
in winter from north-east India, Burma and Thailand, is synonymous with the northern form, B. t.
suschkini. Morphological evidence indicates that B. t. suschkini and B. t. davidi may constitute a
separate, highly migratory species, B. davidi. B. thoracicus {sensu stricto ) is a shorter-distance migrant
which breeds around the southern and eastern flanks of the Tibetan plateau.
INTRODUCTION
The Spotted Bush- Warbler Bradypterus thoracicus is one of the more
widespread and frequently encountered of the Asian Bradypterus. In this
paper, the taxonomy of Bradypterus thoracicus is re-examined with particular
reference to the little-known taxon B. t. shanensis. Primaries are numbered
descendently (i.e. from mid-wing outwards) and wing measurements taken
by the maximum chord method. BM is the Natural History Museum,
Tring, U.K.; MCZ is Museum of Comparative Zoology, Harvard,
Massachusetts; USNM is National Museum ofNatural History, Washington,
D.C., ZIAS is Zoological Institute, Academy of Sciences, St Petersburg.
Bradypterus thoracicus has an apparently disjunct distribution: the races
kashmir ensis, thoracicus and przevalskii are distributed along the Himalayas
and around the north-eastern margins of the Tibetan Plateau to north-
central China. Two other races are known from northern Asia: suschkini
occurs from the northern Altai eastwards to north-eastern Baikal while
davidi is found from south-eastern Transbaikalia to Amurland and Manchuria
(Watson et al. 1986). Davidi is also listed as breeding in Hebei province,
northern China (Cheng 1987; Figure 1) and probably also breeds in
adjacent Shanxi province where a few singing males were heard by Mikael
Kail in June 1991 and by Per Alstrom in June 1993. Several singing males
have also been observed in central and north-western Sichuan during 1 989-
1994 by P. Alstrom and U. Olsson (Per Alstrom, in litt.), constituting a
major extension of the known range.
The seasonal distribution of these forms is not well understood. In the
Himalayas, the nominate race is said to breed between 2,400 m and 3,600
m (Ali and Ripley 1987) though Inskipp and Inskipp (1991) mention a nest
with eggs as high as 4,850 m. It breeds in scrub and herbage near the treeline
and is an altitudinal migrant, wintering down to the plains. It inhabits low
160
P. D. ROUND and V. LOSKOT
Forktail 10
Photos 1 and 2. B. t. shanensis trapped at Bung Boraphet, Nakhon Sawan province, 12 February
1981. (Specimen no. DSM 509; photo: Philip Round).
Photo 3. B. i. shanensis trapped at Bung
Boraphet, Nakhon Sawan province, 14
February 1981. (Specimen no. DSM 525;
photo: Philip Round).
Photo 4. B. t. davidi trapped at Beidaihe, Hebei
province, 19 May 1991. Adult male, sexed on song
(photo Peter Kennerley). Note that the rufous tones
have been exaggerated during the reproduction of
this slide.
scrub, rank grass and tangled herbage fringing the forest as well as irrigated
crops (Ali and Ripley 1 983) . In Nepal, it winters in waterside vegetation and
in reedbeds and elephant grass along rivers (Inskipp and Inskipp 1991; C.
Robson pers. comm.). Cheng (1987) shows B. t. przevalskii as occurring
from Qinghai to Gansu and northern Sichuan and B. t. thoracicus from
Xizang Autonomous Region (Tibet) to Sichuan, Yunnan, Guizhou and
Guangxi Zhuang Autonomous Region but does not indicate any separate
breeding and winter ranges.
The northern forms, suschkini and davidi , inhabit moist taiga, forest
glades and open grassy areas with scattered bushes (Dement’yev and
Gladkov 1 968). Davidi is also found in damp areas on scrubby hillsides in
northern China (La Touche 1925-1934). Both are summer visitors, though
in neither is the winter range known. Dement’yev and Gladkov (1968) state
that suschkini winters in China, and davidi in southern China, although this
is not corroborated by Cheng (1987). Birds are said to return to their
breeding grounds in southern Transbaikalia and the Altai during the second
1994
A reappraisal of the taxonomy of the Spotted Bush-Warbler
161
Figure 1. Map lo show approximate known ranges of taxa under consideration.
half of June (Dement’yev and Gladkov 1968). Away from its breeding
grounds, davidi is only known from specimens collected on migration: in
Shandong province (Cheng 1987) and in Hebei province, where a few
individuals have recently been observed and netted in both spring and
autumn (M. Williams in litt.) It appears to be a late spring migrant there,
passing through chiefly in late May (P. Alstrom in litt.).
THE STATUS OF B. t. shanensis
One further race, B. t. shanensis , was first described from a specimen
collected on 20 October 1937 at Maymyo (3,500 ft), Myanmar (Ticehurst
1941). It is also known from Assam, India and Thailand (Watson et al.
1986). Unlike the previously mentioned forms, shanensis is only known
outside the breeding season: the breeding range is said to be ‘possibly in the
mountains of northern Burma’ (Watson et al. 1986).
The majority of records come from Thailand, where, since 1981, it has
been recognised as a common and widespread winter visitor, from the far
north of the country south to at least as far as Rangsit, Pathum Thani
province (14 00’N latitude), a marshy area on the northern outskirts of
162
P. D. ROUND and V. LOSKOT
Forktail 10
Table 1. List of specimens of Bradypterus thoracicus shanensis known from Thailand
1. Doi Langka, Chiang Mai province. 2 May 1931. H. M. Smith. U S. National Museum
(USNM 330868).
2. Doi Suthep, 3,300 ft, Chiang Mai province. 23 March 1937. H. G. Deignan. U.S.
National Museum (USNM 344432).
3. Nong Turn, Chiang Mai province. Plains, ca. 400 m. 21 December 1965 (two
specimens). B. King. U.S. National Museum (USNM 535426, 535427).
4. Bung Boraphet, Nakhon Sawan province. Plains, ca. 30 m. 12 and 14 February 1981
(two specimens). P. D. Round. Thai National Reference Collection, Bangkok (Field
Nos. DSM 509, DSM 525).
5. Ban Tha Ton, Chiang Mai province. Plains, ca. 400 m. 26 February 1982. P. D.
Round. Thai National Reference Collection (Field No. ACW 35).
Table 2. Summary of biometrics and wing formula of taxa studied
Bangkok (Boonsong and Round 1991). It frequents scrub and grassland in
open country, though almost always favours moist areas, such as along the
margins of ponds, streams and canals. Though most abundant in the plains,
it has been recorded up to at least 1,300 m and the fact that, until recently,
it has been overlooked is due to its extremely skulking habits.
All known specimen records of shanensis from Thailand are listed in Table 1 .
One further specimen, (BM1949-WH1-1-13132), collected from the
Bengal Duars, northern West Bengal, India on 13 November 1925 by H.
Whistler, and examined by P. D. R., can also be assigned to this form,
extending its wintering range slightly further west (Figure 1).
Shanensis is distinguished from nominate thoracicus by its whiter breast,
lacking any greyish suffusion, whitish supercilium, fine brownish breast-
spotting and dull olive-brown upperparts lacking any strong rufescent tinge.
1994
A reappraisal of the taxonomy of the Spotted Bush-Warbler
163
Ticehurst (1941) even described the upperparts as olive-grey in shanensis
compared with russet-brown in thoracicus, overstating the difference slightly.
All the shanensis specimens, and all those seen in the field by PDR showed
a mainly or entirely pale, flesh-coloured lower mandible.
Although Deignan (1963) lists nominate thoracicus for Thailand on the
basis of a single specimen collected in the mountains of Chiang Mai
province, this appears to be based on an erroneous identification of
specimen M.C.Z. 196866, placed by Delacour (1952) with Bradypterns
seebohmi; this apparently remained uncorrected in Deignan (1963).
MORPHOLOGY
The Spotted Bush-Warbler is distinguished from its Asian congeners by the
combination of dark brown-centred, sharply and broadly white-tipped
undertail-coverts, and by its relatively short tail. The taikwing ratio of
thoracicus ( sensu lato ) is roughly 0.8-0. 9, so that in general proportions it
somewhat resembles Lanceolated Warbler Locustella lanceolata. Chinese
Bush-Warbler Bradypterns tacsanowskius, Brown Bush-Warbler B. luteoventris
and Russet Bush-Warbler B. seebohmi are markedly longer-tailed. In B.
seebohmi, for example, the taikwing ratio is ca. 1.1 -1.2 (Round 1992).
Many of the differences among the various forms of Bradypterns thoracicus
have been well described ( e.g ., Sushkin 1925, Stegmann 1929). These races
fall into two morphologically distinguishable groups.
1 . The ‘thoracicus group’, comprising the races thoracicus , kashmirensis and
przevalskii.
The members of this group are relatively large: the wing lengths of
specimens measured ranged from 51.0-59.5 mm (mean 55.1, n = 14) in
thoracicus', 54.0-57.0 (mean 55.9, n = 5) in kashmirensis and 54.6-58.0
(mean 56.3, n = 1 1) in przevalskii (Table 2). The wing is, however, rather
strongly rounded, most obviously so in the nominate race in which the tip
of the 9th (second outermost) primary usually falls opposite the tips of the
secondaries or innermost first or second primaries (only exceptionally the
third innermost primary). The 8th primary shows a substantial shortfall
from the wingtip (0. 5-2.0 mm shorter; average 1.1 mm shorter). The
outermost primary is long, 7 . 0- 1 1 . 5 mm (average 9.5 mm) longer than the
longest primary covert (Table 2), or roughly half the length of the 9th
primary. The races kashmirensis and przevalskii which are distributed to the
west and east respectively of the nominate race, and which extend somewhat
further north, show slightly less rounded wings. This is more obvious in
przevalskii, which has a slightly shorter outermost primary (average 8.0 mm
longer than longest primary covert) and a slightly longer 9th primary, with
the tip usually falling opposite the tip of the third primary. This minor
distinction is mentioned in Vaurie (1959).
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P. D. ROUND and V. LOSKOT
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All three forms can usually be discerned from the members of the
succeeding group on plumage. In all three, the upperparts are generally
warm, dark rufous-brown, (though slightly less so in kashmirensis and
przevalskii than in thoracicus ); the supercilium is greyish (though often
whitish in front of, or above, the eye; P. Alstrom, in litt.); the sides of the
throat and the breast, especially in the centre of the breast below the lower
margin of the spotted gorget, is also strongly washed greyish. The throat and
breast spotting is normally bold and the spots are blackish. The ear-coverts
and sides of the neck are usually grey, though slightly lighter grey in
przevalskii than in thoracicus (Sushkin 1925).
2. The “davidi group”, comprising the races davidi and suschkini
These two forms differ substantially from the thoracicus group of races on
both biometrics and plumage. They are markedly smaller, having an
average wing length of 52.9 mm (range 5 1 .0-56.7 mm, n = 8) in davidi and
52.5 mm (range 50.3-54.9 mm, n = 6) in suschkini (Table 2). In addition,
both have a slightly more pointed wing: the tip of the 9th primary falls
opposite the tips of primaries 3-5 while the 8th primary is subequal to the
wingpoint, ranging from 0 mm to 0.8 mm shorter. The outermost primary
is much shorter, only 5. 4-8.0 mm longer than the primary coverts (average
6.0 mm) in davidi and 3. 8-7. 2 mm (average 5.3 mm in suschkini ; Table 2).
Both davidi and suschkini have less rufescent-tinged upperparts than the
members of the thoracicus group and are somewhat colder, more olive-
brown above. Both show a mainly buffy or sometimes whitish supercilium
and brownish ear-coverts and sides of neck. While the differences between
the two are very slight, suschkini is slightly paler and more pure brown and
warmer-toned on the upperparts than davidi, has a whiter and bolder
supercilium, and the spots on the throat and upper breast are browner and
less clearly marked. There is considerable variation in the strength of the
spotting in both forms, though. The type specimen of davidi at MCZ
showed slightly blacker, bolder spotting than the paratype while among
specimens of both davidi and suschkini in ZIAS, the spots were generally
browner and sparser among juveniles and females.
Davidi may show a very slight greyish tinge on the ear-coverts and throat
or breast (which is always lacking in suschkini ) but this is always much less
marked than in the thoracicus group.
Both davidi and suschkini art additionally distinguished from the thoracicus
group in always showing a brownish (rather than greyish) wash across the
breast below the lower margin of the gorget. On the basis of extensive
experience of thoracicus and davidi, both in the field and in the hand, P.
Alstrom (in litt.) has commented that the thoracicus group is characterised
by grey supercilium, ear-coverts, sides of neck and centre of breast and, (in
thoracicus, but not przevalskii) by sometimes showing a forecrown which is
slightly more rufous than the rest of the upperparts. In davidi, the ear-
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A reappraisal of the taxonomy of the Spotted Bush-Warbler
165
figure 2. Scatter plot ot wing length and length of outermost primary for taxa under consideration.
• thoracicus
o kashmirensis
A przevalskii
□ shanensis
plO length (mm) * „
Wing length (mm)
coverts, sides of neck and centre of breast are brown (sometimes faintly
grey-tinged), the supercilium is buffy-tinged and there is no contrast
between the forecrown and the rest of the upperparts.
THE POSITION OF B. t. shanensis
On the basis of both its measurements and its plumage features, shanensis
closely resembles the northern forms, davidi and suschkini. The wing length
of shanensis (average 51.4 mm; range 50.0-53.0 mm, n = 8) was not
significantly different from either davidi or suschkini (P > 0.1 and P > 0.2
respectively; two-sample r-test). The length of the outermost primary in
shanensis (average 5.9 mm longer than the primary coverts; range 4. 0-8.0,
n = 7; Table 2) also differed from neither of the other two forms (P > 0.7
and P > 0.4). By contrast, shanensis differed very significantly in both
measurements from each of the members of the thoracicus group (P< 0.01;
two-sample r-test)). A bivariate scatter plot shows an almost complete
separation between davidi , suschkini and shanensis on the one hand, and the
members of the thoracicus group on the other (Figure 2).
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P. D. ROUND and V. LOSKOT
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On other features of wing formula, namely position of the tip of 9th
primary, and shortfall of 8th primary from the wingpoint, shanensis likewise
resembled davidi and suschkini.
The plumage features of shanensis also showed a close correspondence
with those of davidi and suschkini in being colder, more olive-brown on the
upperparts (instead of dark rufescent-brown as in thoracicus)-, in having a
whitish supercilium and brown ear-coverts. Shanensis typically shows rather
weak spotting on the throat and upper breast. Of a total of eight shanensis
examined, either as actual specimens or as photographs of specimens, two
bore only very slight traces of spotting while the remainder were all more or
less distinctly spotted, though the spotting was weaker and browner than in
davidi. The weaker throat spotting of shanensis was closely similar to one of
six suschkini specimens held at the Academy of Sciences, St. Petersburg.
All of the features which serve to distinguish davidi from nominate
thoracicus, mentioned by La Touche (1923, 1925-34) and Vaurie (1959),
apply equally to shanensis : namely, the short outermost primary (less than
half the length of the second outermost); the whitish supercilium and the
generally whitish underparts with a brownish, rather than grey wash on the
breast.
A direct comparison of one of the Thai shanensis specimens with a series
of both davidi and suschkini at ZIAS showed that shanensis more closely
resembled suschkini rather than davidi in respect of the weaker breast
spotting, and on the basis of its greater development of rufous, ochre shades
on both upperparts and underparts, especially on the sides of the neck,
flanks and undertail-coverts.
MANDIBLE COLOURATION
The most consistent difference between shanensis on the one hand, and
davidi and suschkini on the other, was in the colouration of the lower
mandible. Shanensis shows a mainly or entirely pale, flesh-coloured lower
mandible, whereas both the type and paratype of davidi, as well three out of
five adult davidi and four out of five adult suschkini, including the type, at
the Academy of Sciences, St. Petersburg showed dark lower mandibles.
Such a difference, however, can evidently be accounted for by seasonal
variation in bare part colour. The type and paratype of davidi were collected
on 1 June and 31 May respectively (La Touche 1923) and the type of
suschkini on 5 July (Stegmann 1 929) whereas all specimens of shanensis were
collected during the period October to early May. Moreover, a juvenile
davidi collected by La Touche in September showed a mandible which was
‘flesh-coloured, shading to yellow at its base and with dark point’ (La
Touche 1925-34). Of the specimens at ZIAS, two davidi, collected on 18
July and 4 August, and one suschkini, collected on 4 August, exhibited a pale
basal part of the mandible with only the tip dark. A juvenile suschkini and
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A reappraisal of the taxonomy of the Spotted Bush-Warbler
167
Figure 3. Sonagrams of songs of three of the taxa under consideration:
(a) B t. davidi , Huzong. Greater Xingan Mountains. Heilongjiang, Peoples Republic of China. June 1988
(Per Alstrom). (b) B. t. suschkini , Listivijanka. Lake Baikal. Russia, June 1986 (Per Alstrom). (c) B t.
shanensis , Huai Kha Khaeng Wildlife Sanctuary. Uthai Thani province, western Thailand. 15 January 1983
(P. D. Round)
a juvenile davidi, collected on 17 August and 22 September respectively,
each showed an entirely pale mandible.
Seasonal variation in the colour of the lower mandible may be typical
among Brady pterus (with the exception of Brown Bush- Warbler B. luteoventris,
which shows an entirely pale lower mandible throughout the year; Round
1992). Although most specimens of nominate thoracicus in BMNH showed
a blackish lower mandible, this again seems to be a reflection of the fact that
they were collected during the spring and summer. Some specimens, most
of which were juveniles, showed a pale lower mandible.
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P. D. ROUND and V. LOSKOT
Forktail 10
VOCALIZATIONS
Supporting evidence linking shanensis with the northern forms, suschkini
and davidi, comes from vocalizations. Both northern forms sing with a
monotonous, buzzing series of notes described as ‘ dzzzzzzr , dzzzzzzr....'
for suschkini (Mild 1987, Figure 3). Davidi sounds virtually identical
(Figure 3). The song lies in the frequency range 4. 5-6. 5 khz, with an interval
of roughly 0. 5-0.7 seconds between notes. Each ‘ dzzzzzzr ’ note is about 0.4
seconds in duration and usually repeated 5-20 times in each song sequence.
Different sequences follow on rapidly from each other, usually with a pause
of no more than one second separating them.
Shanensis observed in Thailand in winter, often gave an almost identical
‘ dzzzzzzr ’ vocalization (described as ‘dzeenk’’ in Boonsong and Round
1991; Figure 3), save that the interval between the notes was longer, usually
8-15 seconds and fewer notes, usually only three to five, were given per
sequence. A lower intensity form of song would be consistent with birds in
winter quarters.
By contrast, birds heard and tape-recorded in central China by both C.
Robson and P. Alstrom, and said to comprise examples of both nominate
thoracicus and przevalskii (P. Alstrom in litt.) sang with a quite different and
diagnostic song described as a rhythmic 'trick-i-di, trick-i-di' (C. Robson) or
usually 'tri-tri-tri-tree' , and sometimes ‘ tri-tri-tree' (P. Alstrom).
Unfortunately, there appear to be no recordings of undoubted nominate
thoracicus from the Himalayas for comparison.
DISCUSSION
The various forms of Bradypterus thoracicus (sensu lato) fall into two distinct
‘subspecies groups’.
1 . The rounded-winged, thoracicus group of races, including nominate
thoracicus, kashmirensis and przevalskii, which have a mainly Sino-Himalayan
distribution. These forms are shorter-distance and altitudinal migrants,
which presumably explains their more rounded wing. The tendency to a
slightly less rounded wing in both kashmirensis and przevalskii, evident in a
slightly longer eighth primary and a slightly shorter outermost primary, may
perhaps be explained by their more westerly and northerly distributions,
respectively, necessitating a slightly longer migration than thoracicus, which
occupies the central, most southern portion of the range of the group. The
limits of the ranges of thoracicus and przevalskii appear to be imperfectly
defined, since the ranges given in Cheng (1987) and Watson et al. (1986)
imply possible sympatry in Sichuan and northern Yunnan, which could not
normally be countenanced for two subspecies. If, as seems very likely, the
variation among the members of the thoracicus group is clinal, there should
1994
A reappraisal of the taxonomy of the Spotted Bush-Warbler
169
be a zone of intergradation between nominate thoracicus and przevalskii in
central China within which it might not be easy to assign individual
specimens to one form or the other.
2 . The races davidi, suschkini and shanensis, which are characterised by their
smaller size and more pointed wing than the members of the preceding
group. On first examination, the position of shanensis appears anomalous
since on the basis of both biometrics and plumage it clearly belongs with
suschkini and davidi rather than with thoracicus, yet its breeding grounds are
said to be ‘possibly in the mountains of northern Burma (Watson et al.
1986), i.e. somewhere within the breeding range of nominate thoracicus.
Since shanensis is only known in winter, all records coming from the period
October to May, whereas davidi and suschkini are known only on, or in the
vicinity of, their breeding grounds across Transbaikalia and northern
China, most or all records coming from the period May to August, the
conclusion that shanensis is synonymous with either or both forms is
compelling. Supporting evidence comes from the very abundance of
shanensis , which is a common winter visitor throughout most of continental
Thailand (Boonsong and Round 1991). Such abundance might be expected
of a form with an extensive breeding range across northern Asia, but would
be less likely of a form supposedly with a relatively restricted Sino-
Himalayan or north Burmese breeding range.
Shanensis, therefore, is merely a synonym of suschkini which it more
closely resembles on plumage than davidi. It can probably be assumed that
davidi ( sensu stricto ), the more easterly-breeding form, winters further to the
east, probably in Indochina. Yet it is surprising that davidi has not yet been
recorded on passage away from north-east China, particularly Hong Kong.
The fact that ‘ shanensis ’ shows generally weaker throat and breast spotting
than suschkini would suggest that there may be seasonal variation in thn
character, in which case winter davidi, showing weaker spotting than
breeding birds, might be overlooked among suschkini/ shanensis. It would be
desirable to obtain further specimens from Thailand in order to fully
examine the range of variation, as well as to search for wintering birds in
Indochina.
The degree of separation between these two groups on biometrics alone
strongly suggests that Bradypterus thoracicus ( sensu lato ), could be be a
composite of two distinct species, one of which comprises the Sino-
Himalayan forms, (nominate thoracicus, kashmirensis and przevalskii) while
the other comprises the northern, highly migratory forms, davidi and
suschkini, and includes shanensis which is synonymous with suschkini. Any
formal assignation of species limits should, however, await evidence from
studies on behaviour and vocalisations, preferably involving playback
experiments. If this hypothesis were proven, suschkini and davidi should be
united as Bradypterus davidi, since davidi (La Touche 1923) is the senior
name.
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P. D. ROUND and V. LOSKOT
Forktail 10
We thank the staff of the Sub-department of Ornithology, The Natural History Museum, Tring and
Dr. Niphan Ratanaworobhan, Thailand Institute of Scientific and Technological Research, Bangkok,
for permission to examine specimens in BM and the Thai National Reference Collection respectively.
Dr. Raymond A. Paynter, Jr., kindly supplied photographs and biometrics of the type and paratype
of B. davidi in the Museum of Comparative Zoology, Cambridge, Massachusetts. Dr. Bruce Beehler
supplied photographs and biometrics from specimens of shanensis in the U.S. National Museum. Per
Alstrom provided tapes of the songs of davidi and suschkini while Dr. J.W. Hardy, Curator of
Ornithology and Bioacoustics, Florida State Museum, kindly produced the sonagrams. The
Alexander Library, Edward Grey Institute of Field Ornithology, Oxford provided photocopies of
some key references.
We thank Per Alstrom and Craig Robson for providing much useful discussion based on their
observations in western China. Craig Robson also independently examined and photographed the
shanensis specimens in the Smithsonian Institution on our behalf while Peter Colston kindly checked
the numbers of some specimens in the BM. Peter Kennerley kindly permitted us to use his
photograph of davidi from north-east China, and he, Per Alstrom, Warren Brockelman and Craig
Robson all commented on drafts of this manuscript. Dr Sangvorn Kitthawee gave statistical advice.
REFERENCES
Ali, S. and Ripley, S. D. (1983) Handbook of the birds of India and Pakistan. Compact Edition. Oxford:
Oxford University Press.
Boonsong Lekagul and Round, P. D. (1991) A guide to the birds of Thailand. Bangkok: Saha Karn
Bhaet.
Cheng Tso-hsin (1987) A synopsis of the avifauna of China. Beijing: Science Press.
Deignan, H. G. (1963) Checklist of the birds of Thailand. Bull. U.S. Nat. Museum 226. Washington,
D.C.: Smithsonian Institution.
Delacour, J. (1952) The specific grouping of the bush warblers Bradypterus luteoventris, Bradypterus
montis and Bradypterus seebohmi. Ibis 94: 362-263.
Dement’yev, G. P. and Gladkov, N. A., eds. (1968) Birds of the Soviet Union, 6. Jerusalem: Israel
Program for Scientific Translations.
Inskipp, C, and Inskipp, T. (1985) A guide to the birds of Nepal. London: Croom Helm.
La Touche, J. D. D. (1923) Description of Tribura thoracica davidi. Bull. Brit. Om. Cl. 43: 1 68-169.
La Touche, J. D. D. (1925-34) A handbook of the birds of eastern China, 1 . London: Taylor and Francis.
Mild, K. (1987) Soviet Bird Songs. Stockholm. Two cassettes and booklet.
Round, P. D. (1992) The identification and status of the Russet Bush-Warbler in China and
continental Southeast Asia. Hong Kong Bird Report 1991: 188-194.
Stegmann, B. (1929) Neue Formen aus Ost-Sibirien. J. Om. 77: 249-250.
Sushkin, P. (1925) Notes on systematics and distribution of certain Palaearctic birds. Proc. Boston
Soc. Nat. Hist. 38: 1-55.
Ticehurst, C. B. (1941) Systematic notes on Indian birds, 10. Ibis (14)5: 318.
Vaurie, C. (1959) The birds of the Palearctic fauna. Passeriformes. London: Witherby.
Watson, G. E., Traylor, M. A., Jr., and Mayr, E. (1986) Family Sylviidae, Old World warblers. Pp.
3-294 in E. Mayr and G. W. Cottrell, eds., Check-list of birds of the world, 11. Cambridge,
Massachusetts : Museum of Comparative Zoology.
Philip n. Round, Center for Conservation Biology, Faculty of Science, Mahidol University, Rama 6 Road,
Bangkok 10400, Thailand.
V. Loskot, Zoological Institute, Academy of Sciences, 1 99034, St. Petersburg - 34, Russia.
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A reappraisal of the taxonomy of the Spotted Bush-Warbler
171
APPENDIX
Biometrics and wing formula for all specimens examined
172
P. D. ROUND and V. LOSICOT
Forktail 10
m = male; f = female; u = unsexed. Primaries numbered descendantly; ss indicates tip of 9th primary falls opposite
tips of secondaries; p3/4 indicates tip of 9th primary falls between 3rd and 4th primaries, etc. WP = wing-point; n.r.
= not recorded Specimens in ZIAS measured by VL; those in MCZ by R.A. Paynter, Jr. and those in USNM by B.
Beehler. All others by PDR.
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Sightings of two rare raptors, Lesser
Spotted Eagl e Aquila pomarina and Pied
Harrier Circus melanoleucos , in Pakistan
WILLIAM S. CLARK and ALEEM AHMED KHAN
Roberts (1991) reported only a single sight record in Pakistan for Pied
Harrier Circus melanoleucos , and an unconfirmed sight record for Lesser
Spotted Eagle Aquila pomarina. Thus it was with great interest that we saw
and identified an individual of each species during January 1993. Clark later
sighted another Lesser Spotted Eagle at Rawal Lake, the location of the
original sight record. In addition, three Lesser Spotted Eagle specimens
that were taken in Pakistan during the last century were examined in the
Museum of Natural History at Tring, U.K.
The sightings were made during field trips conducted as part of a raptor
field identification course being taught by the senior author.
A Lesser Spotted Eagle was seen at the Chashma barrage on the Indus
River on 22 January 1993. It was seen first in the morning perched atop a
6 m high tree on a long narrow man-made spit or spur that extends into the
lake behind and just west of the barrage. The eagle flushed as we
approached and flew around us and landed in another tree behind our
vehicle. We turned around and approached it slowly until we could see it
clearly in the telescope. It was the dark brown colour typical of Aquila eagles.
In flight it showed whitish patches at the base of the primaries on the
upperwings, whitish uppertail-coverts, and a small white spot in the middle
of its back. Its upperwing-coverts were a paler brown and contrasted with
the darker brown back and flight feathers. While gliding, its wings were held
bowed, with the wrists held above the body and the wingtips pointed
downward. All of these are characters of Steppe Eagles Aquila nipalensis in
their third summer plumage. We were unable to see the underwing. It
flushed as we approached it closer and flew away across the lake.
We studied various guides, as we were not completely satisfied with the
tentative identification as Steppe Eagle. We noted from Porter et al. (1981)
that Lesser Spotted Eagle can also show the white mid-back patch but, since
Tawny Eagle A. rapax was not covered in this guide, we did not know
whether that species could show such a feature. We decided to return and
look at the eagle again, concentrating on leg feathering, underwing pattern,
and nostril shape.
Luckily, when we returned, it was perched again on the peninsula atop
another tree. Over the next half-hour we observed it from a distance though
a telescope. The stovepipe legs and rather narrow beak were observed, but
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the nostril shape could not be determined. After we approached near
enough to flush it, the underwing pattern was seen clearly as it flew around
us. The pale brown underwing coverts and darker flight feathers it showed
were typical of the Lesser Spotted Eagle. Both Tawny and Steppe Eagles
were eliminated from consideration by observed characters; both would
show longer leg feathers and different underwing patterns. Tawny would
show darker secondaries that contrast with paler inner primaries, and
Steppe would show paler secondaries with a dark subterminal band, as well
as whitish streaks on the greater underwing coverts (shown in figs. 31 and
32 in Porter et al. 1981). Greater Spotted Eagle A. clanga was considered
and rejected because it is almost always overall a darker brown and has a
noticeably larger head with shaggy nape feathers; features lacking on the
eagle in question. Khan has several colour photographs showing this bird
in flight at a distance.
The senior author is extremely familiar with Lesser Spotted Eagles of the
race hastata from many sightings in India; and also of the nominate race
from more than five years of field work in Israel, including handling live eagles .
The only previous sight record of the Lesser Spotted Eagle in Pakistan was
one seen on 3 March 1988 at Rawal Lake near Islamabad by Hirschfeld et
al. (1988). Clark visited this lake on 27 January 1993 and observed a bird
of this species soaring around over the lake. It was identified by its wing
shape and underwing pattern; identity was later confirmed by distant colour
photographs. At the same time there were several Steppe Eagles and many
Black Kites Milvus migrans soaring also. The Lesser Spotted was not seen
close to the Steppe Eagles but was seen with Black Kites. It appeared
somewhat bigger than them, but not as much larger as did the soaring
Steppes, when compared later to nearby Black Kites.
Clark found three specimens of Lesser Spotted Eagle in the Museum of
Natural History, Tring (Nos. 85.8.19.1192; 85.8.19.1193; 85.8.19.1194)
that had been collected in Pakistan. All had been taken by W. H. Unwin in
May 1870 in the Agrove valley of North West Frontier Province; two were
labelled as adult male and adult female, presumably a mated pair.
An adult female Pied Harrier was observed in flight for approximately
5 min on 24 January 1993, approximately 50 km west of Dera Ismail Khan.
It was first seen harassing a Western Marsh-Harrier C. aeruginosus , compared
to which it was somewhat smaller. We noted that its uppersides were
brownish-grey with a noticeable white patch on the uppertail-coverts and
that its underwings were very whitish with faint dark markings, lacking wide
black markings on the wingtips. Its underbody was whitish with dark
markings on the breast, but its belly was rather unmarked. The wingtips
were rounded, quite unlike the pointed appearance of those of Pallid
Harriers Circus macrourus and Montagu’s Harriers C. pygargus. The above
characters eliminate all age and sex classes of the other five species of
harriers that occur in the Indian subcontinent and fit exactly the adult
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female of this species. We have several colour photographs showing this bird
in flight at a distance.
The senior author is familiar with Pied Harriers from repeated sightings
during autumn migration at Beidaihe, China and a small number of
sightings in India and Nepal.
There are two previous records for the Pied Harrier in Pakistan: a male at
Lahore on 27 December 1973 (Vittery 1993), and an adult male seen in
December 1985 and January 1986 at Uchchali lake in the Salt Range
(Roberts 1991).
The authors are grateful to David Ferguson, U. S. Fish & Wildlife Service, and Mumtaz Malik, North
West Frontier Province Forestry Department, for arranging the raptor field identification course. T.
J. Roberts and E. Hirschfeld gave helpful comments on earlier drafts.
REFERENCES
Hirschfeld, E., Kjellen, N. and Ullman, M. (1988) Birdwatching in Pakistan. Published privately.
Porter, R. F., Willis, I., Christensen, S. and Nielsen, B. P. (1981) Flight identification of European
raptors. Third edition. London: Poyser.
Roberts, T. J. (1991) The birds of Pakistan , 1. Oxford: Oxford University Press.
Vittery’, A. (1993) The birds of Pakistan: supplementary observations from the northern Punjab and
hills. Forktail 9: 143-147.
William S. Clark, 7800 Dassett Court, Apt 101, Annandale, VA 22003, USA.
Aleetn Ahmed Khan, WWF-Pakistan, Ali Industrial Technical Institute, Ferozepur Rood, P. O. Box 5180.
Lahore 54600 Pakistan.
Horned Grebe Podiceps auritus: a new
species for India
R. DRIJVERS
On 28 December 1 993 I noticed a small grebe swimming on the Kosi River
near Ramnagar in Uttar Pradesh, northern India.
The bird was easily identified as a winter-plumaged Horned Grebe
Podiceps auritus by its small size, flat crown, black cap sharply demarcated
from the white cheeks, pale lores, and its stubby, pale-tipped bill.
Subsequently it was also observed by D . van den Schoor and photographed
by G. Bellens and R. van der Elst ( O.B.C . Bull. 19: 66).
This constitutes the first record of Horned Grebe for India and only the
fourth or fifth for the Indian subcontinent. The other records were all in
Pakistan: one (unconfirmed) on Zangi Nawar lake, Baluchistan on 17
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January 1984; two on Band Kushdil Khan lake, Baluchistan on 20 January
1984; one on Kund lake, Hab Chowki, Lasbela in March 1986; and two on
Khabbaki lake, Salt Range in January 1987 (Roberts 1991).
REFERENCE
Roberts, T. J. (1991) The birds of Pakistan, 1. Oxford: Oxford University Press.
Eyebrowed Thrush Turdus obscurus: a
new species for Sri Lanka
OLE F. JAKOBSEN
On 5 February 19941 observed an Eyebrowed Thrush Turdus obscurus when
visiting Victoria Park in Nuwara Eliya Town (6°58’N 80°55’E), Sri Lanka.
The observation was made from 1 7h00 to 1 7h30 on the east side of the Park
near Park Road at 1 900 m. The thrush, observed at a distance of 6-7 m, was
first moving around on the ground (10 minutes), and thereafter perching on
a branch (5 minutes). The weather was overcast with a soft drizzle of rain.
I used Bushnell 9x36 binoculars. Notes were taken and the bird described
as follows: size like that of Pied Thrush Zoothera wardii (seen 15 minutes
earlier in the Park); upperparts uniform pale brown; supercilium, which
extended from bill to side of nape, white and very prominent; lores dark with
a short white line underneath; malar stripe grey with a white line above; side
of head uniform pale grey; chin white and throat uniform pale grey like side
of head; upper breast, sides of breast and flanks uniform pale reddish brown;
belly white; tarsus yellowish; bill yellowish and iris dark.
I had no doubt that it was a thrush and was right from the beginning aware
of the significance of the observation. I am familiar with Eyebrowed Thrush
from several observations in Malaysia and the Philippines. However, to rule
out any possible confusion with other thrushes, Ali and Ripley (1983) was
consulted on the spot and the other references below after having returned
home. From the literature it was obvious that no other thrush has the
combination of uniform pale grey throat and uniform reddish brown breast
together with a prominent white supercilium.
This is the first record of Eyebrowed Thrush for Sri Lanka. The species
is a common winter visitor from the breeding-grounds in Siberia (Yenisey
east to Sea of Okhotsk, south to Lake Baikal) to southern Japan, southern
China, north-east India, the Philippines, South-East Asia and the Greater
Sundas. Eyebrowed Thrush has also straggled to Europe, Arabia, Alaska
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(Cramp 1988), north-east Sulawesi and Flores (White and Bruce 1986),
and elsewhere in the Indian subcontinent: South Andaman Island and north
Karnataka (Ali and Ripley 1973), Nepal (Inskipp and Inskipp 1991),
Madras, Tamil Nadu (Santharam 1985) and the Maldives (Ash, this issue).
The species was feeding on open ground free of herbs, but with some leaf
litter, in the same area as an Indian Pitta Pitta brachyura and a Spot-winged
Thrush Zoothera spiloptera (though not seen together). This habitat was
shaded by dense trees and bushes and some parts of it were used as a dump
for garden compost. The thrush was turning over dead leaves, probably in
search for invertebrates.
The bird was seen later by other observers and remained until at least 28
February (T. Loseby).
I thank S. W. Kotagama and B. O. Poulsen for their comments on the manuscript.
REFERENCES
Ali, S. and Ripley, S. D. (1973) Handbook of the birds of India and Pakistan, 9. Bombay: Oxford
University Press.
Ali, S. and Ripley, S. D. (1983) A Pictorial Guide to the Birds of the Indian Subcontinent. Bombay:
Oxford University Press.
Ash, J. S. (1994) Birds of the Maidive Islands, Indian Ocean. Forktail 10.
Cramp, S., ed. (1988) The birds of the Western Palearctic, 5. Oxford: Oxford University Press.
Dement’ev, G.P. and Gladkov, N. A. (1968) Birds of the Soviet Union, 6. Jerusalem: Israel Program
for Scientific Translations Ltd.
King, B. F., Dickinson, E. C. and Woodcock, M. W. (1975) A field guide to the birds of South-East Asia.
London: Collins.
Meyer de Schauensee, R. (1984) The birds of China. Oxford: Oxford University Press.
Santharam, V. (1985) New records - Ashy Minivet and Eyebrowed Thrush in Madras. Newsletter for
Birdwatchers 25(5 & 6): 9-1 1.
White, C. M. N. and Bruce, M. D. (1986) The birds of Wallacea. London: British Ornithologists’
Union.
Wild Bird Society of Japan (1982)H field guide to the birds of Japan. Tokyo: Wild Bird Society of Japan.
Ole F. Jakobsen, Blagardsgade 19, 2. tv., DK-2200 Copenhagen N., Denmark
Red-tailed Tropicbird Phaethon
rubricauda: a new species for Thailand
OLE F. JAKOBSEN
On 3 August 1 990 I was going by motorboat from Laem Phra Nang 8°00’N
98°5 1 ’E to Krabi Town, Krabi Province, Thailand, when I observed a Red¬
tailed Tropicbird Phaethon rubricauda.
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The observation was made 8 km south-west of Krabi Town at 17h00.
Notes were taken and used for the description below. The bird came
towards the boat and passed within 1 2- 1 5 m at a height of 7 m above the sea.
It was seen in good light for about 20 seconds, but without binoculars
because of the very rough sea and a strong south-west monsoon wind. My
attention was attracted by its relatively large size and the big red bill,
reminding me of Caspian Tern Sterna caspia. I quickly realised that it was
a tropicbird, having seen them previously in South America and Africa. I
immediately realised the significance of this record.
The bird, which was about the size of a Caspian Tern, looked all white
except for the rather strong, deep red bill and a distinct black eye-stripe
which extended from in front of the eye to the nape. The pointed tail lacked
elongated central tail feathers. It flew with active wingbeats and some
gliding.
The identification as Red-tailed Tropicbird was checked by consulting
King et al. (1975) and Harrison (1983) was consulted on my return home.
There is no other large, nearly all white species with a deep red bill, black
eye-stripe and wedge-shaped tail. The white plumage without black barring
on the upperparts and black primaries ruled out all species of gulls, terns and
other tropicbirds.
The Red-tailed Tropicbird inhabits the Indian and Pacific Oceans, and is
mainly pelagic outside the breeding season. The nearest breeding sites are
the Cocos (Keeling) Islands, Christmas Island, and Manuk and Gunung
Api in the Banda Sea (MacKinnon and Phillipps 1993). A straggler has
previously reached the Bay of Bengal (Harrison 1983).
This is the first record of Red-tailed Tropicbird for Thailand and the
Malay Peninsula. The species might have been overlooked due to its pelagic
habits; it is probably found near to the coast only after severe storms.
I wish to thank Philip D. Round for his comments.
REFERENCES
Harrison, P. (1983) Seabirds an identification guide. Kent: Croom Helm.
King, B. F., Dickinson, E. C. and Woodcock, M. W. (1975)/! field guide to the birds of South-East Asia.
London: Collins.
MacKinnon, J. and Phillipps, K. (1993) A field guide to the birds of Borneo, Sumatra, Java and Bali.
Oxford: Oxford University Press.
Ole F. Jakobsen, Blagardsgade 19, 2. tv., DK 2200 Copenhagen N, Denmark.
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Japanese Thrush Turdus cardis : a new
species for Thailand
GRAHAM FINCH and MARTIN KENNEWELL
On 3 February 1993, at 07h00, we arrived at the junction of the jeep track
at km 37.5 just past the checkpoint on the main road leading to the summit
of Doi Inthanon. An obvious feature was a small party of Eyebrowed
Thrushes Turdus obscurus feeding in fruiting trees. The majority were in a
tree on the corner of the road to Mae Chaem. Knowing that several other
species of thrush Turdus frequently joined the Eyebrowed Thrushes, it
seemed pertinent to check through these birds.
Almost immediately M. K. had brief views of a thrush which appeared all
dark and showed a grey wash on its flanks. It soon took flight and crossed
the road, showing a white belly and a dark breast; it landed in the tall trees
around the entrance to the jeep track.
G. F. soon relocated the bird in another fruiting tree, where it became
more cooperative, and both of us took down a description. The bird
appeared strikingly marked: the upperparts and head were completely black
and this colour extended down to the upper breast where it was broken by
several pale spots; the belly was unmarked white; the white lower breast and
the grey-washed flanks were liberally marked with black spots, which were
similar in appearance to those on the underparts of a Song Thrush T.
philomelos ; the eye appeared dark and no orbital ring was noted; the bill was
yellow, with a small amount of black on the tip of the culmen; the legs and
feet were also yellow, but of a slightly paler colour than the bill. It was similar
in size to the accompanying Eyebrowed Thrushes but appeared to have a
shorter tail.
Reference to Boonsong and Round (1991) led us to the conclusion that
it was a species not described in that book. We then read through the
descriptions of thrushes in King etal. (1975) and soon established that it was
a male Japanese Thrush T. cardis and presumably the first record for
Thailand.
The bird remained until 1 1 February and was seen by several other
observers, including Mr Daengrassani and Uthai Treesucon (Thailand),
Clive Viney (Hong Kong), Jim Chance (U.S.A.), Paul and Mark McManus
(U.K.) and Raf Drijvers (Belgium).
Many thanks to Philip D. Round for his helpful comments on the manuscript.
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REFERENCES
Boonsong Lekagul and Round, P. D. (1991) A guide to the birds of Thailand. Bangkok: Saha Karn
Bhaet.
King, B. F., Dickinson, E. C. and Woodcock, M. W. (197 5) A field guide to the birds of South-East Asia.
London: Collins.
Graham Finch, 14 Thorndale, Ibstock, Leicestershire LE67 6JT, U.K.
Martin Kennewell, Main Street, South Muskham, Newark, NG23 6EE, U.K.
Rosy Starling Sturnus roseus : a new
species for Thailand
GRAHAM CLARK
On Friday, 28 March 1 986 I was driving north along the shore road at Khao
Sam Roi Yot National Park, Prachuab Khirikhan province (12°08’N
99°59’E). I stopped to look at some waders on the lagoons and, whilst
scanning with my binoculars, examined a line of starlings Sturnidae on a
telephone wire some 40 m away. The small flock was comprised of about 30
Common Mynas Acridotheres tristis, six Asian Pied Starlings Sturnus contra
and another individual which immediately caught my attention because it
was bright pink.
I observed the bird for about 30 secs before it took off and flew east with
the rest of the flock. I obtained the following brief description: size and
structure similar to those of the Asian Pied Starlings alongside, but perhaps
a little smaller; head, throat and upper breast, wings, tail and undertail-
coverts black; mantle, upper breast and belly bright salmon-pink; bill
yellow.
From this brief observation I concluded that it was an adult Rosy Starling
Sturnus roseus. Although I searched for 1 5 minutes amongst the dunes in
which the bird had disappeared it was not seen again.
An adult Rosy Starling, presumed to be a different individual, was seen by
P. D. Round, in mid-May 1986, in the aviary of Siam Farm, an animal
trading company in Bangkok. The proprietor of the company mentioned
that the bird had been trapped in Langsuan district, Chumphon province,
c. 200 km south of Khao Sam Roi Yot.
The species breeds from central and south Russia, and occasionally in
south-east Europe, across central Asia to the Altai mountains and south to
northern Afghanistan (Sibley and Monroe 1990). It winters in the Indian
subcontinent (Ali and Ripley 1987). It is nomadic in its behaviour, frequently
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occurring outside of its normal range and, since it migrates on a north-west
to south-east axis, its occurrence in Thailand is perhaps not surprising.
REFERENCES
Ali, S. and Ripley, S. D. ( 1 987) Compact edition of the handbook of the birds of India and Pakistan. New
Delhi: Oxford University Press.
Sibley, C. G. and Monroe, B. L., Jr. (1990) Distribution and taxonomy of birds of the world. New Haven:
Yale University Press.
Graham Clark, 138/3 Nicolson Street, Edinburgh EH8 9EH, U.K.
Plain Sunbird Anthreptes simplex
feeding on arils of acacia seeds
HUGH A. FORD
Three Plain Sunbirds Anthreptes simplex were seen on the edge of the
Universiti Pertanian Malaysia forest reserve near Ayer Hitam, c. 20 km
south-west of Kuala Lumpur, Peninsular Malaysia on 20 July 1993. They
were identified by their olive upperparts, grey throat, dull yellow underparts,
red eyes and short dark bills. Only one bird had a dark patch on the forehead,
which I did not see reflecting light. As they moved amongst the phyllodes
of acacia trees (. Acacia mangium ) they behaved more like warblers than
sunbirds. When I watched them more closely I realised that they were taking
the orange-red arils which attach the seeds to the pods. Although they were
swallowing the arils I could not see if they also consumed the seeds. One bird
was present for at least 20 minutes.
The aril in acacias is a fleshy appendage which has grown from the apex
of the ovule along the seed stalk. It is often brightly-coloured and is
frequently consumed by insects such as ants; it can contain high
concentrations of fat and protein (Glyphis et al. 1981). Honeyeaters
(Meliphagidae) and a few other birds in Australia consume the red or yellow
funicles of several acacia species (Forde 1986). Acacia cyclops has been
introduced into South Africa from Australia and its arils and seeds are eaten
by a variety of birds there (Middlemiss 1963). Acacia mangium is native to
northern Australia and has been planted widely in South-East Asia for
timber and pulp.
I know of no account of birds consuming acacia arils in South-East Asia,
nor of sunbirds eating them anywhere. However, Plain Sunbirds and
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Purple-naped Sunbirds Hypogramma hypogrammicum have been recorded
eating the fruits of Poikilospermum (Urticaceae) in East Malaysia, and fruit
may be an important food of both species (Lambert 1991). Ornithologists
in the region should look for other birds using this new food source.
REFERENCES
Forde, N. (1986) Relationships between birds and fruits in temperate Australia. Pp. 42-58 in H. A.
Ford and D. C. Paton, eds. The dynamic partnership: birds and plants in southern Australia. Adelaide:
Government Printer.
Glyphis, J. P., Milton, S. J. and Siegfried, W. R. (1981) Dispersal of Acacia cyclops by birds. Oecologia
48: 138-141.
Lambert, F. R. (1991) Fruit-eating by Purple-naped Sunbirds Hypogramma hypogrammicum. Ibis
133: 425-426.
Middlemiss, E. (1963) The distribution of Acacia cyclops in the Cape Peninsula by birds and other
animals. S. Afr. J. Sci. 59: 419-420.
Hugh A. Ford, Department of Zoology' and Animal Ecology/, University of New England, Armidale, NSW
2351, Australia.
The distribution of nests of the Black-
and-Red Broadbill Cymbirhynchus
macrorhynchus along a river in Sarawak
S. J. M. BLABER and D. A. MILTON
The Black-and-red Broadbill Cymbirhynchus macrorhynchusconstructs a
gigantic pear-shaped nest, usually overhanging a river or stream (Medway
and Wells 1976, Smythies 1981) and is most easily seen when travelling by
boat. During the course of fieldwork in the Sri Aman Division of Sarawak
in June and September 1993, counts were made of the number and
distribution of Black-and-red Broadbill nests along the Lingga River.
Counts were from the town of Pantu on the River Seterap to its confluence
with the River Kelauh and thence down the River Lingga until the point it
meets the River Lupar - an overall distance of about 30 km.
During June 1993 a total of 27 nests was counted and they were
distributed as follows:
two nests in the approximately 5 km freshwater zone above the estuary in
the River Seterap suspended from Pandanus vegetation along the bank.
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23 nests in trees of tidally inundated swamp (rain) forest along the river
edge in the tidal reaches of the River Seterap, a distance of about 10 km -
three of the nests had birds in attendance.
two nests in the well developed and tall (up to 25 m) mangroves in the
upper reaches of the Lingga River estuary.
No nests were recorded in the mangroves of the last 10 km or so of the
Lingga River.
During September 1993 only 14 nests were counted and all were in the
riparian swamp forest of the River Seterap. None was observed in the
Pandanus or in the mangroves. Also none of the nests was attended.
From the distribution of nests the species appears to prefer nesting in the
riparian swamp forest. Although the observed distribution could be due to
the greater availability of suitable branches overhanging the water in this
forest, compared with Pandanus , which offers fewer possible nest sites, this
is unlikely to be the reason for few nests occurring in the mangroves. The
mangroves offer a greater variety of potential over-water nest sites but the
vegetation behind the mangroves often consists of secondary forest or
subsistence agriculture. The distribution of nests is perhaps more closely
related to the food requirements of the birds. Suitable fruit and/or insects
for feeding to mates or young in the nest (Lambert 1989) may only occur
in the swamp forest areas . It is also possible that the availability of freshwater
in swamp forests may be important.
Nest records for the Black-and-red Broadbill in Borneo are between
December and August (Fogden 1965, Lambert and Woodcock in prep.);
from Peninsular Malaysia between February and August (Medway & Wells
1 976, Lambert and Woodcock in prep.); from Thailand between April and
June, and from Sumatra from March to June (Lambert and Woodcock in
prep.). Hence the absence of birds around nests during September is not
surprising. However, the reasons for the disappearance of nests between
June and September are obscure. Three other nests of this species occurring
along a forest stream near Lingga persisted over the same period. As this is
a relatively dry time of year, the loss is unlikely to have been due to flooding.
Also, despite the large tidal range (4 to 5 m), all nests were well above the
height of high water springs. It is possible that nests were dislodged by wind
or heavy rain or that they fell victim to predators. Jeyarajasingam (1983)
records the sudden disappearance of the nest of a Silver-breasted Broadbill
Serilophus lunatus which contained young, probably due to predation. A
considerable number of potential bird, reptile and mammalian predators is
present in the Lingga area, such as various raptors, Varanus, snakes, civets
and monkeys. No published records or observations of such predation could
be traced. However, the nests of tropical birds are frequently predated, and
the often nocturnal predators are seldom seen. Removal by humans also
cannot be ruled out, although appears unlikely in this environment.
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REFERENCES
Fogden, M. P. L. (1965) Borneo bird notes. Sarawak Museum J. 12: 395-414.
Jeyarajasingam, A. (1983) Observations on the nest of the Silver-breasted Broadbill (Aves,
Eurylaimidae). Malayan Nat. 37: 14-16.
Lambert, F. R. (1989) Daily ranging behaviour of three tropical forest frugivores. Forktail 4: 107-1 16.
Medway, Lord and Wells, D. R. (1976) The birds of the Malay Peninsula, 5. Conclusion, and survey
of every species. London: H.F. and G. Witherby Ltd.
Smythies, B. E. (1981) The birds of Borneo. Third Edition. Kota Kinabalu and Kuala Lumpur: The
Sabah Society and the Malayan Nature Society.
S.J.M. Blaber, 33 Wuduru Road, Cornubia, Queensland 4130, Australia.
D.A. Milton, 336 Prout Road, Burbank, Queensland 4156, Australia.
Mountain Hawk-Eagles Spizaetus
nipalensis in Viet Nam
G. E. MORRIS
The Mountain Hawk-Eagle Spizaetus nipalensis is thought to be a widespread
migrant in South-East Asia (King et al. 1975), but there are no records for
Viet Nam in the standard work by Delacour and Jabouille (1931), in the
recent checklist for the country (Vo Quy 1983) or from the recent forest
surveys (Robson et al. 1989, 1993a and b). The only record was of one
observed at Tam Dao, north of Hanoi in October 1962 (Fischer 1974).
At 1 5h00 on 2 January 1 992, whilst descending the main track above the
headquarters of the Bach Ma National Park (between Hue and DaNang in
central Annam), I saw an immature Mountain Hawk-Eagle land on the top
of a small tree at an altitude of about 200 m. It was watched for 30 minutes,
using 10x40 binoculars and a 30x75 telescope; the permanently raised
wispy crest, which was black with white tips to the feathers, was clearly
visible. It twice fanned its tail to preen, revealing 8 to 10 narrow, evenly-
spaced black and white bars. When it finally took off and glided in a circle
around me, the projecting head and the very heavy neck were conspicuous,
but the crest was not visible in flight, even at close range. The upperwing was
grey-brown with a lighter area on the primary-coverts, a feature that is also
shown by immature Changeable Hawk-Eagle V. cirrhatus.
This single record might have related to a vagrant to Viet Nam but on 1 0
January 1 992, during a visit to Thao Cam Vien zoo, Ho Chi Minh city, two
immature Mountain Hawk-Eagles were found sharing a cage with five
Changeable Hawk-Eagles. The director of the zoo understood that all of
these birds had been captured in the mountain forests of south Annam (Lam
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Dong province). The exact provenance is not known but the director was
certain that they originated in Viet Nam. In January 1993 only one of the
Mountain Hawk-Eagles was still in the zoo and by January 1994 both had
disappeared. A visit on 17 January 1993 to the shop of a wildlife dealer in
DaLat city centre (Lam Dong province) revealed one stuffed (adult) and
one living Mountain Hawk-Eagle, the latter in a cage at the back of the
premises. The owner of the shop said that they were common in the area and
claimed to have six more at home in her private ‘zoo’. For comparison, other
stuffed raptors on display included a Black Eagle Ictinaetus malayensis , two
Grey-faced Buzzards Butastur indicus and a Barn Owl Tyto alba, none of
which is uncommon in Viet Nam. The owner expected U.S. SI 00 for the
live eagle and seemed accustomed to the negative attitude of European
visitors towards wildlife trading. She was confident that she could sell all of
her stock of live animals and birds to Chinese dealers from Singapore and
Taiwan without any problem.
Finally, on 1 8 December 1 993, another immature Mountain Hawk-Eagle
was seen near Cu Jut, a small town on the main road south-west of Ban Me
Thuot in south Annam. The bird was perched on the top of a tree in an area
of partly-cleared forest and both the crest and pale wing-coverts were clearly
visible.
The species may have been overlooked previously, though it is also
possible that numbers have increased in Viet Nam recently, if only as a
winter visitor. Now that its occurrence in northern, central and southern
Viet Nam is established, even greater care will be needed in field identification
of similar species such as Changeable Hawk-Eagle and Jerdon’s Baza
Aviceda jerdoni.
REFERENCES
Delacour, J. and Jabouille, P. (1931) Fes oiseaux de FIndochine fran^aise, 1 . Paris: Exposition Coloniale
Internationale.
Fischer, W. (1974) Vorlaufiger Abschlussbericht iiber Vogelbeobachtungen in Vietnam. Beitr.
Vogelk. 20: 249-300.
King, B. F., Dickinson, E. C. and Woodcock, M. W. (1975) Afield guide to the birds of South-East Asia.
London: Collins.
Robson, C. R., Eames, J. C., Wolstencroft, J. A., Nguyen Cu and Truong Van La (1989) Recent
records of birds from Viet Nam. Forktail 5: 71-97.
Robson, C. R., Eames, J. C., Nguyen Cu and Truong Van La (1993a) Further records of birds from
Viet Nam. Forktail 8: 25-52.
Robson, C. R., Eames, J. C„ Nguyen Cu and Truong Van La ( 1 993b) Birds recorded during the third
BirdLife/Forest Birds Working Group expedition in Viet Nam. Forktail 9: 89-119.
Vo Quy (1983) [A catalogue of the birds of Vietnam.] Pp. 12-43 in L. N. Medvedev, ed. Fauna and
ecology of the birds of Vietnam. Moscow: Nauka. (In Russian.)
G. E. Morris, Research Division, N. E. Wales Institute, Deeside, Clwyd, CH5 4BR, U.K.
186
INDEX TO FORKTAIL 1 - 9
Forktail 10
Index to Forktail 1-9
INDEX BY FIRST AUTHOR
ALSTROM, P., U. OLSSON and P. D. ROUND. The taxonomic status of Acrocephalus agricola
tangorum. 6: 3-14.
ALSTROM, P. and U. OLSSON. Blyth’s Leaf-Warbler Phylloscopus reguloides found breeding in
Thailand. 9: 150-152.
ANDERSEN, C. Y., M. K. POULSEN, O. F. JACOBSEN and M. HEEGAARD. Observations on
the Luzon Water Redstart Rhyacomis bicolor in the Mount Pulog National Park, Philippines. 7:
147-150.
ASH, J. S. Raptor migration on Bali, Indonesia. 9: 3-12.
BAKEWELL, D. N„ G. J. CAREY, D. G. DUFF, J. PALFERY, A. PARKER and M. D.
WILLIAMS. Observations of Relict Gulls Larus relictus on passage at Beidaihe, People’s Republic
of China. 4: 77-88
BALEN, B. VAN, I. S. SUWELO, D. S. HADI, D. SOEPOMO, R. M. ARLON and MUTIARINA.
The decline of the Brahminy Kite Haliastur indus on Java. 8: 83-88.
BANKS, R. C. The generic name of the Crested Argus Rheinardia ocellaia. 8: 3-6.
BARAL, H. S. and J. C. EAMES. Jerdon’s Babbler Moupinia altirostris a new species for Nepal. 6:
85-87.
BERG, A. B. VAN DEN and C. A. W. BOSMAN. Supplementary notes on some birds of Lore Lindu
Reserve, Central Sulawesi. 1: 7-14.
BIJLSMA, R. G. and F. E. DE RODER. Notes on Nordmann’s Greenshank Tringa guttifer in
Thailand. 2: 92-94.
BOSWALL, J. Ornithology in China: an update. 4: 55-62.
BOSWALL, J. Notes on the current status of ornithology in the People’s Republic of China. 2: 43-
52.
BRAZIL, M. A. and N. MOORES. The importance of Japanese wetlands as wintering grounds for
the endangered Saunders’s Gull Larus saundersi. 8: 1 13-1 17.
BRAZIL, M. A. and H. IKENAGA. The Amarni Woodcock Scolopax mira: its identity and
identification. 3: 3-16.
BRAZIL, M. A. The birds of Shuangtaizihekou National Nature Reserve, Liaoning province, China.
7: 91-124.
CHOUDHURY, A. Bird observations from Sibsagar District, Assam, India. 6: 35-42.
CLARK, W. S. and N. J. SCHMITT. Field identification of the Rufous-bellied Eagle Hieraaetus
kienerii. 8: 7-10.
CLEMENTS, F. A. Recent records of birds from Bhutan. 7: 57-76.
CLEMENTS, F. A. and N. J. BRADBEAR. Status of wintering Black-necked Cranes Grits nigricollis
in Bhutan. 2: 103-107.
COLLAR, N. J., P. D. ROUND and D. R. WELLS. The past and future of Gurney’s Pitta Pina
gurneyi. 1: 29-52.
COOPER, R. J. Spotted Crake Porzana porzana: a new species for Nepal. 6: 89-90.
CUEREL, P. and SOMSRI THONGSATJA. Mallard Anas platyrhynchos: a new species for
Thailand. 8: 151-152.
DE RODER, F. E. The migration of raptors south of Annapurna, Nepal, autumn 1985. 4: 9-18.
DE SILVA, R. I., E. PERERA, L. PERERAand K. SAMARASINGHE. Black Tern Chlidonias niger.
a new species for Sri Lanka. 9: 153-154.
DE SILVA, R. I. and L. PERERA. Long-billed Plover Charadrius placidus : a new species for Sri
Lanka. 9: 154-155.
DEL HOYO, J. and E. CARRERA. Dusting by a Green Cochoa Cochoa viridis. 4: 117.
DICKINSON, E. C. Does the Pied Harrier Circus melanoleucos breed in the Philippines? 1: 85-86.
1994
INDEX TO FORKTAIL 1 - 9
187
DICKINSON, E. C. A review of smaller Philippine swiftlets of the genus Collocalia. 5: 23-34.
DICKINSON, E. C. A review of larger Philippine swiftlets of the genus Collocalia. 4: 19-54.
DICKINSON, E. C. Does the White-eyed River-Martin Pseudochelidon sirintarae breed in China? 2:
95-96.
DUFF, D. G., D. N. BAKEWELL and M. D. WILLIAMS. The Relict Gull Larus relictus in China
and elsewhere. 6: 43-65.
DUTSON, G., R. WILKINSON and B. SHELDON. Hook-billed Bulbul Setoriiis criniger and Grey¬
breasted Babbler Malacopteron albogulare at Barito Ulu, Kalimantan. 6: 78-82.
DUTSON, G. A sighting of Ficedula (crypta) disposiia in Luzon, Philippines. 8: 144-147.
ELKIN, J. A., C. F. MANN and C. OZOG. Black-collared Starling Stumus nigricollis: a new species
for Borneo. 8: 155-156.
ELKIN, J. A. Japanese Night-Heron Gorsachius goisagi: a new species for Borneo. 8: 154-155.
EVANS, T. D„ P. MAGSALAY, G. C. L. DUTSON and T. M. BROOKS. The conservation status
of the forest birds of Siquijor, Philippines. 8: 89-96.
EWINS, P. J., P. D. ROUND and D. R. BAZELY. Urban roosting by Barn Swallows Hirundo rustica
wintering in Thailand. 6: 68-70.
GARDINER, S. Mandarin Duck Aix galericulata: a new species for Nepal. 6: 87-88.
GASTON, A. J. Andrew Leith Adams: a pioneer of Himalayan ornithology. 4: 3-8.
GASTON, A. J., P. J. GARSON and S. PANDEY. Birds recorded in the Great Himalayan National
Park, Himachal Pradesh, India. 9: 45-58.
GREEN, A. J. The biology of the White-winged Duck Cairina scutulata. 8: 65-82.
GREGORY-SMITH, R. Golden-spectacled Warbler Seicercus burkii: a new species for Malaysia. 9:
158.
GRIMMETT, R. and H. TAYLOR. Recent bird observations from Xinjiang Autonomous Region,
China, 16 June to 5 July 1988. 7: 139-146.
HAN LIANXIAN. Wedge-billed Wren-Babbler Sphenocichla humei : a new species for China. 7: 155-
156.
HARRAP, S. Identification, vocalisations and taxonomy of Pnoepyga wren-babblers. 5: 61-70.
HARRISON, C. J. O. A re-assessment of the affinities of some small Oriental babblers Timaliidae.
1: 81-83.
HARTLEY, I. R. and P. J. K. McGOWAN. Moult and biometrics in five birds endemic to Palawan,
Philippines. 6: 74-77.
HAUGE, P., J. TERBORGH, B. WINTER and J. PARKINSON. Conservation priorities in the
Philippine Archipelago. 2: 83-91.
HE FEN-QI, ZHANG YIN-SUN, WU YONG and GAO TIE-JUN. The distribution of the Relict
Gull Lams relictus in Maowusu Desert, Inner Mongolia, China. 7: 151-154.
HEATH, P. J. and D. M. THORNS. Bristled Grass Warbler Chaetomis striatus new to and breeding
in Nepal, and its separation from Large Grass Warbler Graminicola bengalensis. 4: 1 18-121.
HEATH, P. J. A Short-billed Minivet Pericrocotus brevirostris nest in Nepal. 4: 1 17-1 18.
HELBIG, A. J. Records of Javan Pond-Heron Ardeola speciosa and Dusky Warbler Phylloscopus
fuscatus in peninsular Malaysia in March 1986. 3: 57-59.
HOLMES, D. R. and J. R. D. WALL. Letter: Setomis criniger, Malacopteron albogulare and
conservation in Indonesia. 4: 123-125.
HOLMES, P. R. and B. J. HATCHWELL. Notes on the ecology of the Little Bittern Ixobrychus
minutus at Haigam Rakh, Kashmir, India. 6: 25-34.
HOLMES, P. R. The avifauna of the Suru River Valley, Ladakh. 2: 21-42.
INDRAWAN, M., W. LAWLER, W. WIDODO and SUTANDI. Notes on a feeding behaviour of
Milky Stork Mycteria cinerea on the coast of Indramayu, west Java. 8: 143-144.
INSKIPP, C. and T. P. INSKIPP. Birds recorded during a visit to Bhutan in spring 1993. 9: 121-
142.
INSKIPP, T. P. and P. D. ROUND. A review of the Black-tailed Crake Porzana bicolor. 5: 3-16.
INSKIPP, C. The ornithological importance of Khaptad National Park, Nepal. 5: 49-60.
188
INDEX TO FORKTAIL 1 - 9
Forktail 10
INSKIPP, C. and T. P. INSKIPP. Birds recorded during a visit to Bhutan in autumn 1991. 8: 97-
112.
INSKIPP, C. and T. P. INSKIPP. Some important birds and forests in Nepal. 1: 53-64.
JEPSON, P. The occurrence of Kessler’s Thrush Turdus kessleri in Nepal. 6: 83-85.
JOHNS, A. D. Effects of selective logging on the ecological organization of a peninsular Malaysian
rainforest avifauna. 1: 65-79.
JOHNS, A. D. Recovery of a Peninsular Malaysian rainforest avifauna following selective timber
logging: the first twelve years. 4: 89-106.
KANNAN, R. Rediscovery of the Oriental Bay-Owl Phodilus badius in peninsular India. 8: 148-149.
KATTI, M., P. SINGH, N. MANJREKAR, D. SHARMA and S. MUKHERJEE. An ornithological
survey in eastern Arunachal Pradesh, India. 7: 75-90.
KHAN, M. A. R. The threatened White-winged Wood Duck Cairina scutulata in Bangladesh. 2: 97-
101.
KING, B. Birds observed at Huang Nian Shan, Mabian county, southern Sichuan, China. 4: 63-68.
KING, B. Birds observed at Dafengding Panda Reserve, Mabian county, southern Sichuan, China.
4: 69-76.
KING, B. and PENG JI TAI. Some bird observations in Ganzi prefecture of extreme north-west
Sichuan province, China. 6: 15-24.
KNOWLER, J. T. Collared Grosbeak Mycerobas affinis: a new species for Thailand. 8: 152-153.
LAMBERT, F. R. Daily ranging behaviour of three tropical forest frugivores. 4: 107-1 16.
LANSDOWN, R. V. Recent extensions in breeding range of the Yellow Bittern Ixobrychus sinensis.
3: 61-63.
LEWIS, A. Asian Stubtail Urosphena squameiceps : a new species for Nepal and the Indian subcontinent.
9: 155.
LEWIS, A. Black-and-yellow Grosbeak Mycerobas icterioides: a new species for Nepal. 9: 156.
MADGE, S. C. Swinhoe’s Snipe Gallinago megala: a new species for Nepal. 4: 121-123.
MALLON, D. P. The winter birds of Ladakh. 3: 27-42.
MANN, C. F. Notable bird observations from Brunei, Borneo. 3: 51-56
MANN, C. F. More notable bird observations from Brunei, Borneo. 5: 17-22.
MANN, C. F. and D. A. DISKIN. Northern Shrike Lanius excubitor a new species for Borneo and
South-East Asia. 8: 153-154.
MANN, C. F. Sunda Frogmouth Batrachostomus comutus, carrying its young. 6: 77-78.
McWHIRTER, D . W. Feeding methods and other notes on the Spoon-billed Sandpiper Eurynorhynchus
pygtneus in Okinawa. 3: 60-61.
MOLLER, E. Feeding technique of a White-browed Crake Porzana cinerea. 7: 54-55.
MUNDKUR, T. Prey items of the Great Thick-knee Esacus recurvirostris. 6: 71-72.
NAKHASATHIEN, S. The discovery of Storm’s Stork Ciconia stormi in Thailand. 3: 43-50.
NOSKE, R. A. Field identification and ecology of the Greater Goldenback Chrysocolaptes lucidus in
Malaysia. 6: 72-74.
OGLE, D. Oriental Plover Charadrius veredus: a new species for Thailand. 7: 156-157.
PALMES, P. and C. BRIGGS. Crab-plovers Dromas ardeola in the Gulf of Kutch. 1: 21-28.
PARKES, K. C. Letter: Was the Chinese White-eyed River Martin an Oriental Pratincole. 3: 68-69.
PRAKASH, V., N. V. PRAKASH and W. S. CLARK. Oriental Honey-buzzard Pemis ptilorhyncus:
a new species for the Andaman Islands. 9: 157-158.
RAHMANI, A. R. Status of the Black-necked Stork Ephippiorhynchus asiaricus in the Indian
subcontinent. 5: 99-110.
REDMAN, N. Two new species of birds for the Philippines and other notable records. 8: 1 19-124.
ROBERTS, T. J. Obituary: Salim Ali, 1896-1987. 3: 70-72.
ROBSON, C. R., J. C. EAMES, NGUYEN CU and TRUONG VAN LA. Birds recorded during the
third BirdLife/Forest Birds Working Group expedition in Viet Nam. 9: 89-120.
ROBSON, C. R„ J. C. EAMES, NGUYEN CU and TRUONG VAN LA. Further records of birds
from Viet Nam. 8: 25-52.
1994
INDEX TO FORKTAIL 1 - 9
189
ROBSON, C. R„ J. C. EAMES, J. A. WOLSTENCROFT, NGUYEN CU and TRUONG VAN LA.
Recent records of birds from Viet Nam. 5: 71-98.
ROBSON, C. R. Recent observations of birds in Xizang and Qinghai provinces, China. 2: 67-82.
ROUND, P. D. Winter records of the Manchurian Reed-Warbler Acrocephalus ( agricola ) tangorum
from Thailand. 9: 83-88.
ROUND, P. D., U. TREESUCON and J. C. EAMES. A breeding record of the Giant Pitta Pitta
caerulea from Thailand 5: 35-48.
ROUND, P. D. and U. TREESUCON. The rediscovery of Gurney’s Pitta Pitta gurney i. 2: 53-66.
SANKAR, K., D. MOHAN and S. PANDEY. Birds of Sariska Tiger Reserve, Rajasthan, India. 8:
'133-141.
SERIOT, J., O. PINEAU, R. DE SCHATZEN and Ph. J. DUBOIS. Black-tailed Crake Porzana
bicolor: a new species for Thailand. 2: 101-103.
SHELDON, F. H. Habitat preferences of the Hook-billed Bulbul Setomis criniger and the White-
throated Babbler Malacopteron albogulare in Borneo. 3: 17-26.
SHOWLER, D. Long-billed Partridge Rhizothera longirostris: a new species for Sabah. 8: 156.
SODHI, N. S. Food-niche relationships of five sympatric north Indian herons. 7: 125-130.
SWENNEN, C. and E. C. L. MARTEIJN. Notes on the feeding behaviour of the Milky Stork
Mycteria cinerea. 3: 63-66.
THOMPSON, P. M„ W. G. HARVEY, D. L. JOHNSON, D. J. MILLIN, S. M. A. RASHID, D.
A. SCOTT, C. STANFORD and J. D. WOOLNER. Recent notable bird records from Bangladesh.
9: 13-44.
TYE, A. and H. TYE. Nepal House Martin Delichon nipalensis new to Thailand. 1: 83-85.
TYLER, S. J. and S. J. ORMEROD. The ecology of river birds in Nepal. 9: 59-82.
TYMSTRA, Y. R. Some bird observations from the lower Apsuwa River, east Nepal. 8: 53-64.
VITTERY, A. The birds of Pakistan: supplementary observations from the northern Punjab and hills.
9: 143-148.
VRETTOS, D. G. Observations on the breeding of the Palawan Blue-Flycatcher Cyomis lemprteri.
9: 148-150.
WATTOLA, G. V. Black-billed Magpie Pica pica: a new species for Thailand. 8: 149-150.
WELLS, D. R., P. D. ROUND and J. SCHARRINGA. New information on the ‘Brown-streaked’
Flycatcher Muscicapa latirostris williamsoni. 1: 15-20.
WILES, G. J. and Y. MASALA. Collapse of a nest tree used by Finch-billed Mynas Scissirostrum
dubiutn in North Sulawesi. 3: 67-68.
WILLIAMS, M. D., G. J. CAREY, D. G. DUFF and XU WEISHU. Autumn bird migration at
Beidaihe, China, 1986-1990. 7: 3-56.
WILLIAMS, M. D., D. N. BAKEWELL, G. J. CAREY and S. J. HOLLOWAY. On the bird
migration at Beidaihe, Hebei province, China, during spring 1985. 2: 3-20.
ZACHARIAS, V. J. and A. J. GASTON. The birds of Wynaad, southern India. 8: 1 1-24.
ZHANG YIN-SUN, DING WEN-NING, BU HE and TIAN LU. Breeding ecology of the Relict
Gull Larus relictus in Ordos, Inner Mongolia, China: 7: 131-138.
ZHANG YIN-SUN and HE FEN-QI. A study of the breeding ecology of the Relict Gull Larus relictus
in Ordos, Inner Mongolia, China. 8: 125-132.
ZHANG YIN-SUN, LIU CHANG-JIANG, TIAN LU and BU HE. Recent records of the Relict Gull
Larus relictus in western Nei Mongol autonomous region, China. 6: 66-67.
190
INDEX TO FORKTAIL 1 - 9
Forktail 10
INDEX BY SPECIES MENTIONED IN PAPER TITLE
Acrocephalus ( agricola ) tangorum 9: 83-88.
Acrocephalus agricola tangorum 6: 3-14.
Aix galericulata 6:87-88.
Anas platyrhynchos 8: 151-152.
Ardeola speciosa 3: 57-59.
Batrachostomus comutus 6: 77-78.
Burhinus (= Esacus ) recurvirostris 6: 71-72
Cairina scutulata 2: 97-101; 8: 65-82.
Chaetornis striatus 4: 118-121.
Charadrius placidus 9: 154-155.
Charadrius veredus 7: 156-157.
Chlidonias niger 9: 1 53-154.
Chrysocolaptes lucidus 6: 72-74.
Chrysomrna (— Moupinia) altirostre 6: 85-87.
Ciconia stormi 3: 43-50.
Circus melanoleucos 1: 85-86.
Cochoa viridis 4: 117.
Collocalia 4: 19-54; 5: 23-34.
Cyomis lemprieri 9: 148-150.
Delichon nipalensis 1: 83-85.
Dramas ardeola 1: 21-28.
Ephippiorhynchus asiaiticus 5: 99-1 10.
Esacus recurvirostris 6: 71-72.
Eurynorhynchus pygrnaeus 3: 60-61.
Ficedula (crypta) disposita 8: 144-147.
Gallinago megala 4: 121-123.
Glareola maldivarum 3: 68-69.
Gorsachius goisagi 8 : 154-155.
Graminicola bengalensis 4: 1 18-121.
Grus nigricollis 2: 103-107.
Haliastur indus 8: 83-88.
Hieraaetus kienerii 8: 7-10.
Hirundo rustica 6: 68-70.
Ixobrychus minutus 6: 25-34.
Ixobrychus sinensis 3: 61-63.
Lanius excubitor 8: 153-154.
Larus relictus 4: 77-88; 6:43-65,66-67; 7: 131-
138, 151-154; 8: 125-132.
Larus saundersi 8: 113-117.
Malacopteron albogulare 3: 17-26; 4: 123-125; 6:
78-82.
Moupinia altirostris 6: 85-87.
Muscicapa latirostris williamsoni 1: 15-20.
Mycerobas ajfinis 8: 152-153.
Mycerobas icterioides 9: 156.
Mycteria cinerea 3: 63-66; 8: 143-144.
Pericrocotus brevirostris 4: 117-118.
Pemis ptilorhyncus 9: 157-158.
Phodilus badius 8: 148-149.
Phylloscopus fuscatus 3: 57-59.
Phylloscopus reguloides 9: 150-152.
Pica pica 8: 149-150.
Pina caerulea 5: 35-48.
Pitta gumeyi 1: 29-52; 2: 53-66..
Pnoepyga 5: 61-70.
Porzana bicolor 2: 101-103; 5: 3-16.
Porzana cinerea 7: 54-55.
Porzana porzana 6: 89-90.
Pseudochelidon sirintarae 2: 95-96; 3: 68-69.
Raptors 4: 9-18; 9: 3-12.
Rheinardia ocellata 8: 3-6.
Rhizothera longirostris 8: 156.
Rhyacomis bicolor 7 : 147-150.
Scissirostrum dubiuni 3: 67-68.
Scolopax mira 3: 3-16.
Seicercus burkii: 9: 158.
Setomis criniger 3: 17-26; 4: 123-125; 6: 78-82.
Sphenocichla humei 7: 155-156.
Stumus nigricollis 8: 155-156.
Timaliidae 1: 81-83.
Tringa guttifer 2: 92-94.
Turdus kessleri 6: 83-85.
Urosphena squameiceps 9: 155.
1994
INDEX TO FORKTAIL 1 - 9
191
INDEX BY COUNTRY/REGION
Bangladesh 2: 97-101; 5:3-15,99-110; 9: 13-44.
Bhutan 2: 103-107; 5:3-15,99-110; 7:57-76; 8:97-112; 9: 121-142.
Borneo 3: 17-26; 4: 123-125.
Brunei 3: 51-55; 5: 17-22; 6: 77-78; 8: 153-154, 154-155, 155-156..
China 2: 43-51, 95-96; 4:55-62; 5:3-15; 6:3-13,43-65; 7:155-156.
Hebei province, Beidaihe 2: 3-20; 4: 77-88; 7: 3-56.
Inner Mongolia 6:66-67; 7:131-138,151-154; 8:125-132.
Liaoning province 7: 91-124.
Qinghai Autonomous Region 2: 67-82.
Sichuan 4: 63-68; 4:69-76; 6: 15-24.
Xinjiang Autonomous Region 7: 139-146.
Xizang Autonomous Region 2: 67-82.
Himalayas 4: 3-8.
Hong Kong 6: 43-65.
India 4: 3-8; 5: 3-15, 99-1 10; 7: 125-130; 8: 148-149.
Andaman Islands 9: 157-158.
Arunachal Pradesh 7: 75-90.
Assam 6: 35-42.
Gujarat 1: 21-28; 6: 71-72.
Himachal Pradesh 9: 45-58.
Kashmir 6: 25-34.
Kerala 8: 11-24.
Ladakh 2: 21-41; 3: 27-42.
Rajasthan 8: 133-141.
Indonesia 4: 123-125.
Bali 9: 3-12.
Java 8: 83-88, 143-144;
Kalimantan 6: 78-82.
Sulawesi 1: 7-14; 3: 67-68.
Sumatra 4: 123-125.
Japan 6: 43-65; 8: 113-117.
Amami 3: 3-16.
Okinawa 3: 60-61.
Republic of Korea 6: 43-65.
Laos 5: 3-15.
Malaysia
Peninsular 1: 65-79; 3: 57-59, 61-63, 63-66; 4: 89-106, 107-116; 6: 72-74; 9: 158.
Sabah 3: 61-63; 8: 156.
Mongolia 6: 43-65.
Myanmar 5: 3-15.
Nepal 1: 53-64, 4: 9-18, 117-118, 1 18-121, 121-123; 5: 3-15, 49-60, 61-70, 99-110; 6: 83-85, 85-
87, 87-88, 89-90; 8: 53-64; 9: 59-82, 155, 156.
Pakistan 5: 99-1 10.
Punjab 9: 143-148.
Philippines 1: 85-86; 2: 83-91; 4: 19-54; 5: 23-34; 8: 119-124.
Luzon 7: 147-150; 8: 144-147.
Palawan 6: 74-77; 9: 148-150.
Siquijor 8: 89-96.
Singapore 3: 61-63.
Sri Lanka 5: 99-1 10; 9: 153-154, 154-155.
Taiwan 5: 61-70.
Thailand 1: 15-20, 29-52, 83-85; 2: 53-66, 92-94, 101-103; 3: 43-50; 4: 117; 5: 35-48; 6: 3-13,
68-70; 7: 154-155, 156-157; 8: 149-150, 151-152, 152-153; 9:83-88, 150-152.
U.S.S.R. 6: 43-65.
Viet Nam 5:3-15,71-98; 6:43-8:25-52; 9:89-120.
192
Forktail 10
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Smythies, B. E. (1981) The birds of Borneo. Third edition. Kota Kinabalu and Kuala Lumpur: The Sabah
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