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Peed oo lM rater eS Yh ott ep at tet + z te thy io : Hy Pies Wit @ awry @ i le ny ial u ue hi NA } + ty | ¢ ih : -" “| P g i 1a Ornithologists’ ey Volume 124, No. 1 March 2004 MEETINGS are normally held in the Sherfield Building of Imperial College, South Kensington, London, SW7. The nearest Tube station is at South Kensington; a map of the area will be sent to members, on request. [Limited car parking facilities can be reserved (at a special reduced charge of £5.00), on prior application to the Hon. Secretary]. The cash bar is open from 6.15 pm, and a buffet supper, of two courses followed by coffee, is served at 7.00 pm. (A vegetarian menu can be arranged if ordered at the time of booking). Informal talks are given on completion, commencing at about 8.00 pm. Dinner charges were increased to £19.00, as from Ist January 2004. FORTHCOMING MEETINGS See also BOC website: http://www.boc-online.org Tuesday 27 April—ANNUAL GENERAL MEETING at 6 pm, followed by a Club Social Evening. There will be no speaker, but Members are invited to bring along one or two slides (or a specimen) of a bird of topical interest, and to speak for not more than 5-10 minutes about it. The aim will be to generate discussion, and to facilitate the exchange of information between Members. Applications to Michael Casement including subjects to be raised, and any special facilities required, by 13 April, please. Tuesday 22nd June—Dr P.J.K McGowan ‘Threatened pheasants and partridges in Asia’ Philip McGowan first encountered pheasants in Asia during two months fieldwork to plan the boundaries of the Great Himalayan National Park in Himachal Pradesh, NW India, in February/March 1983. Since then he has carried out surveys and intensive fieldwork on pheasants and partridges elsewhere in northern India, on Palawan in the Philippines, southwest China and in Malaysia. He compiled IUCN Action Plans for three groups of Galliformes and is now the Conservation Director of the World Pheasant Association. His role is to promote action on behalf of the world’s Galliformes, which is amongst the most threatened of avian orders. On the current IUCN Red List 11% of bird species are considered at risk of extinction, whereas for the Galliformes it is 25%. The pressures seem most serious in Asia, where 50% of the world’s pheasant species are listed as threatened. Applications to Tony Statham (Note this change) by 8 June, please. Tuesday 28th September—Professor Glen Chilton - ‘The curse of the Labrador Duck’ Glen Chilton is an Associate Professor of Biology at St. Mary’s College in Calgary, Canada. For the past 18 years, most of his research efforts have concerned the songs of birds, particularly the evolution of songs in crowned sparrows and New World warblers. This work has taken him to some of the most remote parts of North America. He is currently on a research sabbatical in the UK. Nine years ago, while constructing the species account of the extinct Labrador Duck for the Birds of North America series, he became fascinated by the stories associated with this species. They are stories of murder, theft, enormous wealth, and wartime crimes. Glen is now travelling the world to examine all remaining stuffed specimens, and is writing a book about his adventures. Applications to Tony Statham by 14 September please. Future meetings in 2004. The following Tuesdays have been booked: 2 November—Speaker to be arranged 7 December—Speaker to be arranged Overseas Members visiting Britain are especially welcome at these meetings, and the Hon. Secretary would be very pleased to hear from anyone who can offer to talk to the Club, in 2005, giving as much advance notice as possible—please contact: Tony Statham, Woodcock Hill, Durrants Lane, Berkhamsted, Herts. HP4 3TR UK, (or e-mail: SAHS@tinyonline.co.uk) Printed on acid-free paper. Published by the British Ornithologists’ Club Typeset by Alcedo Publishing of Colorado Springs, USA, and printed by Crowes of Norwich, UK Club Announcements Bulletin of the BRITISH ORNITHOLOGISTS’ CLUB Vol. 124 No. 1 Published 5 March 2004 .C. 2004 124(1) CLUB ANNOUNCEMENTS Membership News Hon. Life Member—Rule (3). Congratulations to Bryan Sage after 50 years continuous membership (1954-2004). We regret to report the death (in July 2001) of Dr R.S. Marrus (1994-2001). Hon. Secretary. As announced in BBOC 123 (4), Michael Casement is standing down as Hon. Secretary and, subject to agreement at the AGM (see below), Tony Statham will assume this responsibility as from 1 May 2004; Michael Casement will continue as Hon. Membership Secretary until further notice. Free Membership for Students for 2004. Free membership has been offered, on a trial basis for one year, to suitably qualified students. We are delighted to welcome 41 successful applicants, from a wide spread of countries, with addresses in: UK (5), USA (6), Africa (7), Asia (10—including five from Indonesia), and South and Central America (13). We wish them well in their studies in the coming year. The BOC Website - http://www.boc-online.org The number of enquiries continues dramatically to increase and the major re-design, in 2003, incorporates a number of new features to make it more user- friendly. Do please look at it and let Paul Salaman have your comments. ANNUAL GENERAL MEETING The Annual General Meeting of the British Ornithologists’ Club will be held in the Sherfield Building, Imperial College, London SW7 at 6.00pm on Tuesday 27 April 2004. AGENDA Minutes of the 2003 Annual General Meeting (see Bull. Brit. Orn. Cl. 122 (3): 66—71). Chairman’s report. Trustees Annual Report and Accounts for 2003 (both to be distributed at the meeting). The Bulletin. Editor’s report. Publications report—by Revd. T.W. Gladwin, Chairman JPC The election of Officers. The Committee proposes that: (i) Mr S.A.H. Statham be elected as Hon. Secretary (vice Commander M.B. Casement). (ii) Mr D.J. Montier be re-elected as Honorary Treasurer, (111) Professor R.A. Cheke be elected as Hon. Publications Officer vice J.A. Jobling. (iv) Mr J.P. Hume to be elected vice Mr S.A.H. Statham (v) Commander M.B. Casement, OBE, RN, to continue (ex-officio) as Hon. Membership Secretary. 7. Any other business of which notice shall have been given in accordance with Rule (12). ape Py > The 920th meeting of the Club was held Tuesday 2nd December 2003, in the Sherfield Building Annexe, Imperial College. 23 Members and 9 guests were present. Members attending were: Mrs MLN. MULLER (Chairman), Miss H. BAKER, I.R. BISHOP, Mrs D.M. BRADLEY, Dr.A.P. BUCKLE, Cdr. M.B. CASEMENT RN, Professor R.A. CHEKE, J.B. FISHER, F.M. GAUNTLETT, D. GRIFFIN, J.A. JOBLING (Speaker), R.R. LANGLEY, D.J. MONTIER, Mrs A.M. MOORE (Speaker), Dr. R.P. PRYS- Club Announcements 2 Bull. B.O.C. 2004 124(1) JONES, R.E. SCOTT, P.J. SELLAR, T.R. SMEETON, S.A.H. STATHAM, N.H.F. STONE, C.W.R. STOREY, M.P. WALTERS, and Mrs FE. WARR. Guests attending were: M. BRADLEY, Ms G. BONHAM, Mrs M.H. GAUNTLETT, Mrs M. MONTIER, P.J. MOORE, C.A. MULLER, Mrs S.L. STONE, A.J. WARR, and R.W. WEBSTER. After dinner, Amberley Moore and James Jobling gave a joint presentation entitled ‘The unknown traveller—the ornithological collections of Louis Fraser’. The following is a brief synopsis: Amberley Moore gave a presentation on the life of the Victorian collector Louis Fraser and James Jobling illustrated some of the specimens from Fraser’s collection, now held in the Natural History Museum at Tring. During his lifetime Louis Fraser (1819-—c.1883) was widely acknowledged as an excellent and tireless naturalist and collector. Indeed, because of his attention to detail and breadth of his field notes he has been considered the first of the modern collectors. Of modest education he began work as an office boy at the Zoological Society of London in 1832. By 1841 he had become curator’s clerk and had already contributed five papers to the Proceedings of the Zoological Society of London when, with the influence of the President of the Society Lord Derby, he was appointed naturalist to the ill-fated Niger Expedition, during which he made an important collection of birds and mammals in the Gulf of Guinea. Upon his return in 1842 he was re-employed by the Zoological Society, becoming curator in 1844. He began publication of his Zoologica typica in 1845, illustrating new species of birds and mammals first shown at meetings of the Zoological Society. The financial burden of the series proved to be too great and part XIV, published in March 1849, brought the series to a premature close. Fraser resigned his post in 1846 to take up a six-month contract to collect for Lord Derby in North Africa and on his own account in 1847. He became Temporary Curator of Lord Derby’s collection at Knowsley in April 1848, where he compiled catalogues including a six-volume catalogue of birds (now held in manuscript at Liverpool Museum) and a catalogue of mammals, Catalogue of the Knowsley collection, which he published himself in 1850. He left Knowsley to take up the post of Vice-consul to the Kingdom of Dahomey from 1851 to 1853 during the reign of the notorious King Gezo. In 1857 Philip Lutley Sclater financed Fraser privately to collect for him in South America for three years. During his several journeys abroad Fraser collected over 1,000 specimens from Tunisia, Dahomey [Benin] and the Niger, Fernando Poo [Bioko], Ecuador, Panama, Guatemala and the United States. Over 645 bird specimens collected by Fraser have been identified presently in museum collections in Britain, Germany and the US. They include the type material of over 100 species. Fraser’s name is commemorated in the distinctive Afrotropical flycatcher genus Fraseria Bonaparte, 1854, and his large collections in the Afrotropics and Neotropics gave birth to a raft of eponyms: Deleornis fraseri (Jardine & Selby, 1843); Basileuterus fraseri (Philip Sclater, 1884); Conirostrum (cinereum) fraseri (Philip Sclater 1859); Threnetes (ruckeri) fraseri (Gould, 1861); Oreomanes fraseri Philip Sclater, 1860; Stizorhina fraseri (Strickland, 1844); Zympanistria (tympanistria) fraseri Bonaparte, 1855; and Tityra (inquisitor) fraseri (Kaup, 1852). Opportunity was taken to show slides of many of Fraser’s specimens in the type collection at Tring; such as Cisticola lateralis (Fraser, 1843), Nigrita fusconota Fraser, 1843 and Linurgus olivaceus (Fraser, 1842). Other slides of birds from his collections now held at Tring, Liverpool and Cambridge illustrated his distinctive small circular collectors’ labels often cut from menu cards and sailing dockets! Although Fraser’s earlier career can be verified by official papers and his private correspondence, his latter years are ill-documented. Philip Sclater’s correspondence and papers were kept by his son, William, and it is probable that Fraser’s Ecuadorian correspondence, which must have been extensive, and his field notes, were lost when the Sclater home in London was destroyed by a flying bomb during the Second World War. Fraser’s last written records are found on the labels of three birds taken in Florida in 1883 and now in the UMZ at Cambridge: Carolina Parakeet Conuropsis carolinensis labelled ‘Wekiva River Fl[orid]a Mar. 8 1883’, Roseate Spoonbill Ajaia ajaja labelled ‘Kissimmee River Fl[orid]Ja May 9. 1883’, and Anhinga Anhinga anhinga labelled ‘Sanford Fl{orid]a July 3 1883’. It is probable that Louis Fraser died in North America before 1888, but no record of his death has been found. Club Announcements 3 Bull. B.O.C. 2004 124(1) The 921st meeting of the Club was held Tuesday 20th January 2004, in the Sherfield Building Annexe, Imperial College. 30 Members and | 1 guests were present. Members attending were: Dr C.F. MANN (Chairman), D.N.S. ALLEN, Miss H. BAKER, LR. BISHOP, Mrs D.M. BRADLEY, Dr. A.P. BUCKLE (Speaker), Cdr. M.B. CASEMENT RN, D.R. CALDER, Captain P. CARR RM, S.E. CHAPMAN, Professor R.A. CHEKE, Dr. R.A.F. COX, R.C. DICKEY, FM. GAUNTLETT, A. GIBBS, D. GRIFFIN, Dr. J. GROOMBRIDGE, C.A.R. HELM, J.P. HUME, J.A. JOBLING, R.H. KETTLE, .R. LANGLEY, D.J. MONTIER, Mrs M.N. MULLER, Dr. R.P. PRYS-JONES, N.J. REDMAN, P.J. SELLAR, S.A.H. STATHAM, C.W.R. STOREY, and R.W.WEBSTER. Guests attending were: Ms G. BONHAM, A.J. BRAY, Mrs C.R. CASEMENT, B.J. HUGHES, Mrs M.H. GAUNTLETT, Mrs M. MONTIER, R. RANFT, Mrs W. SPENNING, Dr. FJ. ZINO, (Speaker) Mrs E. ZINO and Miss F. ZINO. After dinner, Frank Zino followed by Alan Buckle gave two splendidly illustrated presentations, under the overall title: Rats on Oceanic Islands—Impacts and Management. The following is a brief synopsis of the two talks: Frank Zino: The rediscovery of Pterodroma madeira When first handled by Padre Ernesto Schmitz in 1903 this bird was identified as Oestrelata feae and, by 1934 when defined by Mathews as a subspecies of Oestrelata mollis, it was thought to be extinct. Schmitz sold many specimens to European museums, including nine of what we now know as Zino’s Petrel Pterodroma madeira. Two more birds were found in 1909 but for decades after that many considered the bird extinct. In October 1940 and October 1951, however, recently fledged birds were attracted to the lights of Funchal and this led Gunther (Jerry) Maul and Alec Zino (PAZ) to think that a colony of P madeira still existed on Madeira. In 1963 Maul organised an expedition to the Selvagem Islands through the Museu Municipal do Funchal (MMF). Christian Jouanin and Francis Roux were on this expedition and awakened the Zino family’s interest in birds. They returned to Madeira over subsequent years and, with PAZ on his yacht Yam Seng, visited many of the islands around Madeira, including Bugio. There, Fea’s Petrel Prerodroma feae was studied and PAZ made excellent recordings of its calls. PAZ reasoned that if P madeira and P feae were so alike their calls might be similar. He played his recording to shepherds from the area where Schmitz had collected his birds and one identified the calls as “the souls of Cidrao”. In April 1969 the approximate breeding area was identified and nests were found the next month. PAZ then left for the Selvagems and should have been accompanied by a French ornithologist, a priest, who missed the boat. On 15 June 1969, the priest went to PAZ’s office and met the men PAZ had organised to search for the breeding birds, who reported finding birds and eggs in burrows. The priest opportunistically organised an expedition the next day using the same men, who had been told not to touch any bird or egg. PAZ returned from the Selvagems late on 15 June and the next day received a call from Pico do Areeiro, saying that they had the birds! He rushed to Areeiro, where he was met by his men with eight birds and six eggs of a species, up to then, considered extinct! After much negotiating, six birds were released. The priest took the eggs, giving one to the MMF (since stolen) and one to PAZ. The next day the Frenchman took another egg and bird. After this disaster, work continued quietly for fear of more collectors. In 1985—86 it was noted that there was no successful breeding on the ledges due to rat predation. We needed outside help and after a fortuitous meeting with Andy Swash of MAFF on Selvagem Grande, he introduced us to Dr Alan Buckle, then at ICI, who came to the rescue, and continues to support us. Alan Buckle: Rodents on oceanic islands—impacts and management Since the earliest days of exploration humans have accidentally, and sometimes purposefully, introduced rodents (mainly Norway Rats Rattus norvegicus, but also Ship or Black Rats Rattus rattus and Polynesian Rats Rattus exulans) to places where they have landed and colonised. On the islands the rodents preyed upon species poorly adapted to withstand their depredations. The full extent of this disaster on the biodiversity of the world’s oceanic islands will never be known but in two recent cases, Lord Howe Island and Big South Cape Island, ornithologists were able to record the rodents’ catastrophic impact on Club Announcements 4 Bull. B.O.C. 2004 124(1) the islands’ avifauna. Many species were extinguished and populations of others decreased dramatically. Thanks to the development of a range of management techniques, pioneered mainly by workers from New Zealand, conservationists now have an ability either to remove alien rodents from islands or, if this is impractical, to control rodents in particularly sensitive areas to allow endangered species a chance to recover. Zino’s Petrel breeds in burrows on cliff ledges among the peaks of Madeira’s central mountain range. During the mid-1980s the birds failed to breed successfully for several years as rats, coming up from the forests below, had infested the breeding ledges. The site was surveyed and, after detailed planning which included an environmental impact assessment, a rodent control programme was initiated to protect the birds. This involved the placement of specially designed rodenticide bait boxes, both in a ‘cordon sanitaire’ around the breeding ledges and on the ledges themselves. The difficult work of maintaining this programme has continued every year since, thanks to the efforts of the Freira Conservation Project and the Natural Park of Madeira (see Zino et al., 2001, Oryx 35: 128-136 and www.pnm.pt). Breeding was at first slow to re-establish but has improved in recent years, with a record in 2003 when > 20 chicks fledged. Different problems faced the workers of the Natural Park of Madeira on Great Salvage Island, 160 nautical miles south of the Madeira mainland. The island was overrun with Rabbits Oryctolagus cuniculi and House Mice Mus sp. A project was initiated in 2002, aimed at the complete eradication of these species from the 240-ha island, in order to protect breeding seabirds and to support application for UNESCO World Heritage Site status. The island is a breeding station for globally important colonies of the White-faced Storm-petrel Pelagodroma marina, Madeiran Storm-petrel Oceanodroma castro, Bulwer’s Petrel Bulweria bulwerii, Little Shearwater Puffinus assimilis and Cory’s Shearwater Calonectris diomedia. Once again, severe difficulties of planning and logistics were overcome to establish and maintain a grid of rodenticide baiting stations over the entire island for more than one year. The rabbits were quickly removed and careful surveys in November 2003 failed to discover any signs of mice. The final outcome of the project, which also involved scientists from the UK Forestry Commission and the University of Reading, is eagerly awaited. The talk concluded with a vigorous and enthusiastic discussion. Robert W. Dickerman 5 Bull. B.O.C. 2004 124(1) Notes on the type of Bubo virginianus sclariventris by Robert W Dickerman Received 8 October 2001; revision received 29 Fanuary 2004 In attempting to make order out of the variation he noted among the 50 pale Great Horned Owls Bubo virginianus from Ontario in the Royal Ontario Museum (ROM), Snyder (1961) divided them into more heavily and less heavily barred groups. Considering the less heavily marked birds to be swbarcticus, he named the darker birds B. v. sclariventris, using a female taken on 26 February 1948 as the holotype. The condition of its gonads was not given. He apparently used only specimens in the ROM, and did not mention the existing types of suwbarcticus and occidentalis. The range of sclariventris was mapped by Karalus & Eckert (1974), Johnsgard (1988) and McGillivray (1989), and the name was used by James (1991) and Pittaway (1993). Godfrey (1986) and Browning (1990) were unable to express an opinion on the validity of sclariventris, and it has not been included in any taxonomic work to date, including Houston et al. (1998) and Konig et al. (1999). Dickerman (1992) studied the series of 60 nesting-season specimens of the subarctic populations in the then National Museum of Canada, Ottawa, and found no distinctive subpopulations, but the Ottawa collection is weak in material from Ontario. To help evaluate the validity of the name sclariventris, James A. Dick and S. Ross James of the ROM selected for me paratype 34,2,2,1 as being most similar to the holotype. I compared it with the types of subarcticus and occidentalis in the Academy of Natural Sciences in Philadelphia. Those two types differ, that of occidentalis being more heavily barred. Giving some allowance for possible spoiling of the specimens due to their different ages (1948 vs 1880), the paratype of sclariventris was a very close match to the holotype of occidentalis. Thus B. v. sclariventris Snyder is a junior synonym of B. v. occidentalis Stone, earlier considered to be a junior synonym of B. v. subarcticus Hoy (Stone 1897, Dickerman 1991). In the absence of adequate nesting-season material, especially from the northern fringes of the range, subarcticus must be used for specimens showing a spectrum of variation in the extent of dark markings, and perhaps in the degree of buffy coloration (Dickerman 1992). If in the future subarcticus is subdivided, close attention must be paid to the differences between the types of subarcticus and occidentalis, both migrants, from Wisconsin and Iowa respectively. Acknowledgments I wish to especially thank J. A. Dick and S. R. James of the ROM for selecting the relevant paratype and for the loan thereof. My gratitude goes to the curators of the several museums where specimens were examined: Academy of Natural Sciences, Philadelphia; American Museum of Natural History, New York; and the National Museum of Natural History, Washington, D.C. Robert W. Dickerman 6 Bull. B.O.C. 2004 124(1) References: Browning, M. R. 1990 Taxa of two North American birds described from 1957-1987. Proc. Biol. Soc. Wash. 103: 432-451. Dickerman, R. W. 1991. On the validity of Bubo virginianus occidentalis Stone. Auk 108: 964-965. Dickerman, R. W. 1992. Additional specimens of the subarctic Great Horned Owl from New York. Kingbird 42: 73-75. Godfrey, W. E. 1986. TheBirds of Canada. Revised edition. National Museum of Natural Sciences, (Canada), Ottawa. Houston, C. S., Smith, D. G. & Rohner, C. 1998. Great Horned Owl (Bubo virginianus). In Poole, A. & Gill, F. (eds.) The birds of North America, no. 372. The Birds of North America, Inc., Philadelphia. James, R. D. 1991. Annotated checklist of the birds of Ontario. Second edn. Life Sciences Miscellaneous Publications, Royal Ontario Museum, Toronto. Johnsgard, P. A. 1988. North American owls, biology and natural history. Smithsonian Institution Press, Washington, D.C. Karalus, K. E. & Eckert, A. W. 1974. The owls of North America (north of Mexico), all of the species and subspecies illustrated in color and fully described. Doubleday & Co., New York. Konig, C, Weick, F & Becking, J.-H. 1999. Owls, a guide to the owls of the world. Pica Press, Robertsbridge. McGillivray, W. B. 1989. Geographic variation in size and reverse size dimorphism of the Great Horned Owl in North America. Condor 91: 777-786 Pittaway, R. 1993. Recognizable forms, subspecies of the Great Horned Owl. Ontario Birds 11: 64-69. Stone, W. 1897. Proper name for the western Horned Owl of North America. Amer. Nat. 31: 236 Snyder, L. L. 1961. On an unnamed population of the Great Horned Owl. Contribution 54: 1-7. Life Sciences Division, Royal Ontario Museum, Toronto Address: R. W. Dickerman, Museum of Southwestern Biology, University of New Mexico, Albuquerque, New Mexico, 87131, U.S.A. Email: bobdickm@unm.edu © British Ornithologists’ Club 2004 Interesting distributional records and notes on the biology of bird species from a cloud forest reserve in north-west Ecuador by Fuan F Freile & Faime A. Chaves Received 1 Fanuary 2003 Even in well-studied countries, such as Ecuador, new distributional records and range extensions are regularly reported as unexplored or poorly known areas are surveyed (e.g. Krabbe 1992, Krabbe et al. 1997, Freile 2001a). In this note we present new records, as well as latitudinal and altitudinal range extensions for several species, taking Ridgely & Greenfield (2001) as our baseline. Our records are based on studies carried out at Bosque Integral Otonga (hereafter Otonga), from March 1999 to February 2002 (see also Chaves 2001). Elevation is given within each species account. Taxonomy follows Ridgely & Greenfield (2001). Juan FE Freile & Jaime A. Chaves 7 Bull. B.O.C. 2004 124(1) Study area Otonga is a private reserve located in north-west Cotopaxi province (00°25’S, 79°00’ W), on the outer slopes of the western Andes, ranging from c.1,300 to 2,200 m elevation. It is located c.5 km west of San Francisco de Las Pampas, in the middle section of the Toachi river drainage, adjacent to the Rio Lelia Protection Forest (c.4,000 ha), and less than 20 km north of the large Los Ilinizas Ecological Reserve (149,900 ha) (Fig. 1). It comprises c.1,000 ha of primary montane cloud forest, secondary forest and some degraded areas (Jarrin 2001). Our surveys were restricted to altitudes above 1,700 m due to the inaccessibility of lower areas. The bird community at Otonga has not been previously studied, but it resembles that of other cloud forest sites further north (Chaves 2001), and especially the avifauna of a site located nearly 30 km to the south, also in Cotopaxi province (Caripero area; N. Krabbe, in /itt. 2003). Vegetation at Otonga is characterised by the diversity and abundance of epiphytic plants, especially bromeliads, aroids and mosses, and by several tree species typical of Andean cloud forests of north-western Ecuador (Jarrin 2001, Nowicki 2001). Figure 1. Map of Pichincha and Cotopaxi provinces, and adjacent areas, north-western Ecuador, showing the Bosque Integral Otonga (large circle, number 1) and other localities mentioned more than once in the text. Scale 1: 2,000.000. 1 Bosque Integral Otonga, 2 Mindo, 3 Reserva Maquipucuna, 4 Tandayapa, 5 Caripero, 6 Palmitopamba, 7 Los Cedros Reserve. Light grey: areas above 1,000 m elevation; dark grey: areas above 2,000 m; blackish grey: Quito city. Juan FE Freile & Jaime A. Chaves 8 Bull. B.O.C. 2004 124(1) Species accounts SEMICOLLARED HAWK Accipiter collaris This rare and Near Threatened, though probably under-recorded hawk is known from very few sites along the Andes of Ecuador, with recent records from the western slope concentrated in the Mindo-Tandayapa area (BirdLife International 2000, Ridgely & Greenfield 2001). At Otonga an Accipiter thought to be this species was recorded on two separate occasions, at 1,900 m elevation. One was seen soaring above a cleared area adjacent to primary forest in July 2000, and one was seen briefly, attacking a flock of Dusky Bush-tanagers Chlorospingus semifuscus, in a secondary forest edge in February 2002. It was distinguished from other Accipiter species that might occur at Otonga (Plain-breasted A. ventralis and Bicoloured Hawks A. bicolor) by its heavily banded underparts (excluding whitish chin and throat) and relatively small size (see Ridgely & Greenfield 2001). It was also distinguished from Micrastur forest-falcons by its smaller size, whitish throat and chin, tail bars of similar length, and because forest-falcons never soar (R. S. Ridgely, pers. comm., 2003). Otonga is located c.60 km to the south of Mindo-Tandayapa area. Further sightings are necessary to confirm its status in the Otonga area. BLACK-AND-CHESTNUT EAGLE Oroaetus isidori At Otonga one was seen attacking a flock of three Sickle-winged Guans Chamaepetes goudotii on 15 December 1999, and in February 2003 one was briefly seen soaring above a largely forested area. This rare and Near Threatened eagle is known from only a handful of sites in the western Andes of Ecuador, primarily from western Pichincha province, but has also been recorded from the Caripero area, 30 km to the south of Otonga (Ridgely & Greenfield 2001). WATTLED GUAN Aburria aburri Several were heard and tape-recorded inside secondary and primary forest from 1,800 to 2,000 m elevation, and occasionally from forest borders along abandoned pasture areas. Vocalisations were not heard between February and March, the wettest months in the area, suggesting either that this species migrates seasonally (see Fjeldsa & Krabbe 1990, Freile 2001b), or that vocal activity is restricted to other months of year. Ranked as Vulnerable in Ecuador and as Near Threatened globally (BirdLife International 2000, Pacheco 2002), there are very few records in the western Andes of Ecuador, wherein it is only known from the Mindo-Tandayapa-Maquipucuna area and from Las Pampas region (Marin et al. 1992, Ridgely & Greenfield 2001). Otonga constitutes its southernmost locality in the western Andes of Ecuador (Ridgely & Greenfield 2001). Hunting of this species in the Otonga area seems very infrequent, as it is fairly common even at forest borders. The presence of this species at Otonga is apparently an indicator of the good condition of forests in the area (N. Krabbe, pers. comm. 2003). Juan F Freile & Jaime A. Chaves 9 Bull. B.O.C. 2004 124(1) DARK-BACKED WOOD-QUAIL Odontophorus melanonotus The distribution of this species extends south to western Cotopaxi wherein it is known from the Otonga and Caripero areas (Ridgely & Greenfield 2001). At Otonga at least seven family groups were regularly recorded along 10 km of transects (in an area of c.100 ha) mainly in continuous primary or secondary forest floor, but also in small remnant patches of forest surrounded by pastureland and sugarcane crops. Most groups constituted one adult male, one adult female and at least two juveniles. On two occasions groups were observed ascending up to 12—13 m into forest sub- canopy before dusk. MAROON-TAILED PARAKEET Pyrrhura melanura Groups of 2—S individuals were recorded at the reserve up to 2,200 m elevation. We recorded it in February 1998, March 1999 and August 1999, but not in September— November 2000 and February 2002, suggesting that it may make seasonal or erratic movements. Flocks were seen eating Ficus spp. (Moraceae) and Alchornea sp. (Rubiaceae) fruits and flying over both forested and open areas. Previously only reported up to 1,900 m in western Ecuador (Ridgely & Greenfield 2001), in the Caripero area (R. S. Ridgely, pers. comm., 2003). LITTLE CUCKOO Piaya minuta One was seen at close range perching in 4-m tall bushes and in a secondary forest border on 20 February 2002, at 1,900 m elevation. In western Ecuador this species has been reported up to 1,500 m (at Mindo and Maquipucuna, see Ridgely & Greenfield 2001; and at Palmitopamba and Los Cedros Reserve, pers. obs.). As the Little Cuckoo was not recorded during previous visits to Otonga, it may not be resident. It has been seen occasionally around Tandayapa Bird Lodge, Pichincha province, up to 1,750 m (R. S. Ridgely, pers. comm., 2003). RUFESCENT SCREECH-OWL Owtus ingens colombianus Otonga constitutes the southernmost site for this taxon in the western Andes of Ecuador (Fitzpatrick & O’ Neill 1986, Freile & Chaves 1999), but is within the range estimated by Krabbe et al. (1998). The taxon colombianus has previously been considered as a species (Krabbe et al. 1998, Freile & Chaves 1999), an opinion supported by its vocalisations (N. Krabbe, in /itt. 2003). OILBIRD Steatornis caripensis The Oilbird is a scarce and local species, with records scattered throughout the Ecuadorian Andes (Ridgely & Greenfield 2001). At Otonga flocks of 4-20 were seen and tape-recorded in September—October 2000, foraging at primary forest tree fall gaps, at 2,000—2,100 m. Birds were seen taking fruits of Nectandra sp. (Lauraceae) and Wettinia sp. (Arecaceae). Its presence at Otonga is apparently seasonal, being apparently absent from December through August. Juan F Freile & Jaime A. Chaves 10 Bull. B.O.C. 2004 124(1) GREEN-FRONTED LANCEBILL Doryfera ludovicae This hummingbird was previously known to occur up to 1,700 m on the western slope of the Andes (1,900 m on the eastern slope) (Ridgely & Greenfield 2001). At Otonga we mist-netted one female on a secondary forest ridge at 2,100 m elevation, on 26 February 2002. This was the only record of this inconspicuous species in the reserve, suggesting that it is either not numerous or it undertakes seasonal movements. EMPRESS BRILLIANT Heliodoxa imperatrix Ranked as Vulnerable within Ecuador (Ortiz-Crespo 2002), due to habitat loss within its limited distribution, and because of its relative natural rarity (Ridgely & Greenfield 2001), this striking hummingbird is known from very few sites in the western Andes of Ecuador, south to northern Pichincha province (Mindo area) (Ridgely & Greenfield 2001, Ortiz-Crespo 2002). At Otonga we mist-netted two females inside primary and secondary ridge-top forests at 2,100—2,200 m, and observed one adult male feeding on introduced Abutilon sp. (Malvaceae) and native plants (families Solanaceae and Rubiaceae) along a secondary forest border. Our record at Otonga constitutes a 60 km southward range extension. GORGETED SUNANGEL #Heliangelus strophianus Near endemic to the north-western Andes of Ecuador. Its distribution extends continuously to northern Cotopaxi and apparently patchily south to El Oro province (Ridgely & Greenfield 2001); however, this might be due to poor knowledge and under-collecting in the central portion of the western Andes of Ecuador (N. Krabbe, pers. comm. 2003). At Otonga it was frequently recorded between 1,800 and 2,200 m elevation in primary and secondary forests, as well as forest borders and partially deforested areas. It was seen feeding on several plant species, especially on bromeliads (Guzmania variegata, G. squarrosa and Tillandsia truncata; see Castaneda 2001), and Abutilon sp. (introduced Malvaceae), an unidentified Solanaceae, Posoqueria sp. (Rubiaceae), another species of Rubiaceae and three species of Gesneriaceae. A nest, found in July 2000, was a shallow cup constructed mainly of moss and fine plant fibres, attached with spider web fibres, and was well hidden under a wet rocky wall 2.3 m above ground. It contained two eggs. This species has not been accorded any threat status to date. Nevertheless, we suspect it should be ranked as Near Threatened as it occurs in a very restricted distributional range (both altitudinal and latitudinal), and apparently prefers forested areas (at least is more numerous there), which are currently being destroyed at a fast rate (Sierra ef al. 1999). WHITE-FACED NUNBIRD Hapaloptila castanea Previously recorded from very few sites in western Ecuador south to western Pichincha province (Tandayapa-Mindo area) and from a few sites along the eastern slope of the Andes (Ridgely & Greenfield 2001). At Otonga it was apparently rare Juan FE Freile & Jaime A. Chaves 11 Bull. B.O.C. 2004 124(1) (<10 records during our three-year study), between 1,800 and 2,100 m altitude, and found only inside primary and tall secondary forest. Otonga represents the southernmost site for this species in western Ecuador, > 60 km south of Tandayapa- Mindo. According to the ranges estimated by Krabbe ef a/. (1998), northern Cotopaxi province (c.20 km south of Otonga) may be the southern limit of its distribution in western Ecuador, but there are no confirmed records there to date (R. S. Ridgely, pers. comm. 2003). Ridgely & Greenfield (2001) suggested that this species should be considered Data Deficient because it occurs at low densities along its whole range, even being absent from apparently suitable areas. We suggest that it should actually be ranked as Vulnerable within Ecuador (and Near Threatened globally?) due to its fairly limited distribution over an area with heavy human pressure (see Sierra ef al. 1999), its preference for forested areas, and its probable natural rarity. It is currently known from a few privately protected forests in Ecuador (Cerro Golondrinas, Maquipucuna, Bellavista, Otonga, San Isidro), but its presence in the Sistema Nacional de Areas Protegidas (National Protected Areas Network) is not yet confirmed. TOUCAN BARBET Semnornis ramphastinus This species is frequently found along forested areas in the western Andes of northern Ecuador and southern Colombia, south to northern Cotopaxi province (Ridgely & Greenfield 2001). At Otonga it was numerous inside primary and secondary forests, as well as along forest borders and open areas with tall standing trees, between 1,700 and 2,200 m. It was seen feeding on fruits of several tree species, but Cecropia spp. (Cecropiaceae; two species) and Ficus spp. (Moraceae; three species) were the most important food resources (for which this barbet is an important seed disperser; Chaves 2000). Although fairly numerous along its range, it is currently ranked as Near Threatened in Ecuador (Freile 2002) and globally (BirdLife International 2000). RUSTY-WINGED BARBTAIL Premnornis guttuligera In western Ecuador known from a handful of sites in western Pichincha province (Ridgely & Greenfield 2001), but its range has been estimated to extend south to northern Cotopaxi province (Krabbe et al. 1998), even though it has not been recorded in the Caripero area, 30 km south of Otonga, at appropiate elevations (R. S. Ridgely, pers. comm. 2003). At Otonga it was found inside primary and secondary forests between 1,900 and 2,200 m, mainly through mist-netting. It was occasionally seen accompanying mixed-species understorey flocks, but also in pairs or alone foraging at low heights in dense clumps of mosses and dead leaves. Otonga represents the southernmost site for this species in the western Andes, but gives further support to the range estimated by Krabbe et al. (1998). Two additional records from north- western Ecuador at Intag Cloud Forest Reserve, Imbabura province (1,850 m) and Chilma Alto, Carchi province (2,200—2,300 m) (J. Nilsson, pers. comm. to R. S. Ridgely) also fill in the apparent discontinuity in this species’ distribution. Juan F Freile & Jaime A. Chaves 12 Bull. B.O.C. 2004 124(1) TAWNY-THROATED LEAFTOSSER Sclerurus mexicanus This widespread species was previously known to occur in Ecuador locally up to 1,500 m (< 1,650 m in the eastern Andean slope) (Ridgely & Greenfield 2001). At Otonga a pair was seen inside primary forest at 2,000 m in September 2000. In February 2002 one was mist-netted, measured and photographed at 1,850 m. The only additional high-altitude record of which we are aware comes from the Tandayapa region, where it has also been recorded up to 2,000 m (M. Tellkamp, pers. comm. 2002). SPILLMANN’S and NARINO TAPACULOS Scytalopus spillmanni and S. vicinior These two species replace each other altitudinally along the Andes of north-western Ecuador and south-western Colombia, with Spillmann’s inhabiting higher altitudes than Narifo (Ridgely & Tudor 1994, Ridgely & Greenfield 2001). At Otonga both species have been recorded from 1,900 up to 2,200 m inside primary and secondary forest, particularly in dense understorey, tree fall gaps and bamboo stands. Although they did not share territories or differ significantly in habitat choice, these two species showed a wider (300 m) altitudinal overlap at Otonga than recorded elsewhere (Krabbe & Schulenberg 1997, N. Krabbe, pers. comm. 2002). They responded to playback of each others’ song, but Narifio Tapaculo was on average less aggressive. Natural features of the forest, such as ridgetops, tree fall gaps, trails, large dead logs or ravines were often the limits of territories. This intricate pattern of ecological overlap deserves further research to understand how these species segregate under syntopic situations (if they actually exclude each other). Similar patterns are also shown by several other tapaculo species (Krabbe & Schulenberg 1997), with altitudinal replacements and suture zones, rather than habitat segregation, being the most common situation (N. Krabbe, pers. comm. 2002). BRONZE-OLIVE PYGMY-TYRANT Pseudotriccus pelzelni Its distribution in western Ecuador is discontinuous, but the gap between southern Pichincha and northern Azuay provinces (Ridgely & Greenfield 2001) may be due to lack of collecting there. At Otonga this species was recorded frequently inside primary and secondary forests, particularly in dense understorey areas as re-growth tree fall gaps, between 1,800 and 2,000 m elevation. The Rufous-headed Pygmy- tyrant P. ruficeps, was also recorded at Otonga, but at slightly higher altitudes than the Bronze-olive. Although were not able to determine if both species were occurring in syntopy, overlap seems plausible as both were recorded at the same elevation (2,000 m), and in close proximity. This site is located c.30 km south of previously known records in northern Ecuador. GREY-BREASTED MARTIN Progne chalybea Several were observed flying above cleared areas on 22—23 February 2002, up to 1,750 m elevation. This numerous and widespread martin is more frequent at lower altitudes, but seems to undertake seasonal migratory movements (Ridgely & Juan F Freile & Jaime A. Chaves 13 Bull. B.O.C. 2004 124(1) Greenfield 2001). It was not recorded on our previous visits to Otonga or on subsequent days, suggesting that it is not a regular visitor or breeding species in the area. Unusually warm weather on the days of observations (pers. obs.) may account for its presence in the area. BLACK-CHINNED MOUNTAIN-TANAGER Anisognathus notabilis In Ecuador this species is mostly restricted to the north-west where it is known from few localities, but is also known from a few sites in the south-west (Ridgely & Greenfield 2001). At Otonga it was frequently found in primary and secondary forests, and in forest borders and open areas with tall standing trees, between 1,900 and 2,200 m. It was less numerous than the Blue-winged Mountain-tanager Anisognathus somptuosus, but it was regularly found accompanying mixed-species canopy flocks, and often only with A. somptuosus. The apparent absence of this species between Cotopaxi and El Oro provinces is possibly due to poor knowledge of this area (N. Krabbe, pers. comm. 2002). YELLOW-BELLIED SISKIN Carduelis xanthogastra There are few records of this species in western Ecuador (Ridgely & Greenfield 2001). Our only record at Otonga in three years was of two female-plumaged birds on 23 February 2002, perching and feeding in an isolated Mimosa tree in a degraded area next to a flowing stream, at 1,700 m. They were identified by the olive-coloured upperparts and foreparts, extending down to lower chest, and by the contrasting yellow wing patch ‘uniformly’ shaped (Ridgely & Greenfield 2001). Yellow-bellied Siskin may be either increasing in the north-western slopes of the Ecuadorian Andes, as suggested by Ridgely & Greenfield (2001), or it may make seasonal or nomadic movements along altitudinal or latitudinal gradients. A record from the Otonga area is mentioned in Ridgely & Greenfield (2001), but we are not aware of its source. Other records The Appendix below lists the birds we recorded at Otonga, including some endemics of the Choco or West Slope of the Andes Endemic Bird Areas, as well as other threatened and Near Threatened species, both at national and global scales (BirdLife International 2000, Ridgely & Greenfield 2001, Granizo et al. 2002). Information on some of them (e.g. Cloud-forest Pygmy-owl Glaucidium nubicola and Moustached Antpitta Grallaria alleni) is published elsewhere (e.g. Freile & Renjifo 2003, Freile et al. 2003). Acknowledgements We are grateful to Richard Mellanby for his permanent support to our research at Otonga, and to the Royal Geographic Society and Glasgow Natural History Society for financial support. Thanks to Giovanni Onore for allowing us to work at Otonga, and especially to César Tapia and his family for taking care of the reserve and for their help and companionship in the field. Thanks to Gabriela Castaneda, Tatiana Santander, Fabian Cupueran, José Hidalgo and David Parra for their help gathering field data, and to Juan F Freile & Jaime A. Chaves 14 Bull. B.O.C. 2004 124(1) Esteban Guevara, Gabriel Iturralde, Pilar Jiménez, Daniela-Rosero, Juan Fernando Andrade, Anna Schubert and Montserrat Bejarano for field assistantship. Thanks also to Markus Tellkamp and Stewart White for sharing their field observations, and to Mauricio Vargas at MECN for letting us visit the bird collection. Niels Krabbe and Robert S. Ridgely kindly reviewed a previous draft of this paper and helped improve it. References: BirdLife International. 2000. Threatened birds of the world. BirdLife International & Lynx Edicions, Cambridge & Barcelona. Castafieda G., G. 2001. Aves asociadas a plantas epifitas de un bosque nublado en la reserva de bosque integral Otonga, noroccidente de Ecuador. Pp. 327—334 in Nieder, J. & Barthlott, W. (eds.) Epiphytes and canopy fauna of the Otonga rain forest (Ecuador). Botanische Insitut der Universitat Bonn, Bonn. Chaves, J. A. 2000. Seleccion de habitat y conducta alimenticia de aves frugivoras endos bosques nublados de las estribaciones occidentales de los Andes del Ecuador. Biology Thesis, Departamento de Biologia, Pontificia Universidad Catolica del Ecuador, Quito. Chaves, J. A. 2001. Comparacion de avifaunas en dos bosques nublados del Choco ecuatoriano. Pp. 311-326 in Nieder, J. & Barthlott, W. (eds.) Epiphytes and canopy fauna of the Otonga rain forest (Ecuador). Botanische Insitut der Universitat Bonn, Bonn. Fitzpatrick, J. W. & O’Neill, J. P. 1986. Otus petersoni, a new screech-owl from the Eastern Andes, with systematic notes on O. colombianus and O. ingens. Wilson Bull. 98: 1-14. Fjeldsa, J. & Krabbe, N. 1990. Birds of the high Andes. Zoological Museum, University of Copenhagen and Apollo Books, Svendborg, Denmark. Freile, J. F. 2001a. Extension altitudinal en la distribucion del Hormiguero Lunulado (Gymnopithys lunulata) en Ecuador. Ornitologia Neotropical 12: 183-185. Freile, J. F 2001b. Registro altitudinal inusual de la Pava Carunculada Aburria aburri en Ecuador. Cotinga 15: 63-64. Freile, J. F. 2002. Barbudo Tucan, Semnornis ramphastinus. Pp. 375 in Granizo, T., Pacheco, C., Ribadeneira, M. B., Guerrero, M. & Suarez, L. (eds.) Libro rojo de las aves del Ecuador. Simbioe, Conservacion Internacional, EcoCiencia, Ministerio del Ambiente & UICN, Quito. Freile, J. F & Chaves, J. A. 1999. Photospot: Colombian Screech-owl, Otus ingens colombianus. Cotinga 12: 95—96. Freile, J. F & Renjifo, L. M. 2003. First nesting records of the endangered Moustached Antpitta in the central Andes of Colombia and western Andes of Ecuador. Wilson Bull. 115: 11-15. Freile, J. F, Chaves, J. A., Iturralde, G. & Guevara, E. 2003. Notes on the distribution, habitat and conservation of the Cloud-forest Pygmy-Owl (Glaucidium nubicola) in Ecuador. Ornitologia Neotropical 14: 275-278. Granizo, T., Pacheco, C., Ribadeneira, M. B., Guerrero, M. & Suarez, L. (eds.). 2002. Libro rojo de las aves del Ecuador. Simbioe, Conservacion Internacional, EcoCiencia, Ministerio del Ambiente & UICN, Quito. Jarrin V., P. 2001. Mamiferos en la niebla. Otonga, un bosque nublado del Ecuador. Publicacion Especial 5. Museo de Zoologia, Centro de Biodiversidad y Ambiente, Pontificia Universidad Catolica del Ecuador, Quito. Krabbe, N. 1992. Notes on distribution and natural history of some poorly known Ecuadorean birds. Bull. Brit. Orn. Cl. 112: 169-174. Krabbe, N. & Schulenberg, T. S. 1997. Species limits and natural history of Scytalopus tapaculos (Rhinocryptidae), with descriptions of the Ecuadorian taxa, including three new species. Pp. 47-88 in Remsen, J. V. (ed.). Studies in Neotropical ornithology honoring Ted Parker. Ornithological Monographs No. 48. American Ornithologists Union, Washington. Krabbe, N., Poulsen, B. O., Frolander, A. & Rodriguez Barahona, O. 1997. Range extensions of cloud forest birds from the high Andes of Ecuador: new sites for rare or little-recorded species. Bull. Brit. Orn. Cl. 117: 248-256. Juan F Freile & Jaime A. Chaves 15 Bull. B.O.C. 2004 124(1) Krabbe, N., Skov, F., Fjeldsa, J. & Petersen, I. K. 1998. Avian diversity in the Ecuadorian Andes. An atlas of distribution of Andean forest birds and conservation priorities. Centre for Research on Cultural and Biological Diversity of Andean Rainforests (DIVA), DIVA Technical Report No. 4, Ronde, Denmark. Marin, M. A., Carrion B., J. M. & Sibley, F.C. 1992. New distributional records for Ecuadorian birds. Ornitologia Neotropical 3: 27-34. Moore, J. V., Coopmans, P., Ridgely, R. S. & Lysinger, M. 1999. The birds of northwest Ecuador, volume I: the upper foothills and subtropics. John V. Moore Nature Recordings, San Jose, California. Nowicki, C. 2001. Epifitas vasculares de la Reserva Otonga. Pp. 115—160 in Nieder, J. & Barthlott, W. (eds.) Epiphytes and canopy fauna of the Otonga rain forest (Ecuador). Botanische Insitut der Universitat Bonn, Bonn. Ortiz-Crespo, F. 2002. Brillante Emperatriz, Heliodoxa imperatrix. Pp. 255—256 in Granizo, T., Pacheco, C., Ribadeneira, M. B., Guerrero, M. & Suarez, L. (eds.) Libro rojo de las aves del Ecuador. Simbioe, Conservacion Internacional, EcoCiencia, Ministerio del Ambiente & UICN, Quito. Pacheco, C. 2002. Pava Carunculada, Aburria aburri. Pp. 215 in Granizo, T., Pacheco, C., Ribadeneira, M. B., Guerrero, M. & Suarez, L. (eds.) Libro rojo de las aves del Ecuador. Simbioe, Conservacion Internacional, EcoCiencia, Ministerio del Ambiente & UICN, Quito. Ridgely, R. S. & Tudor, G. 1994. The birds of South America, vol. 2. Univ. Texas Press, Austin. Ridgely, R. S. & Greenfield, P. J. 2001. The birds of Ecuador. Cornell Univ. Press, Ithaca, New York. Sierra, R., Campos, F. & Chamberlin, J. 1999. Areas prioritarias para la conservacion de la biodiversidad en el Ecuador continental. Un estudio basado en la biodiversidad de ecosistemas y su ornitofauna. Ministerio de Medio Ambiente, Proyecto INEFAN/GEF-BIRF, EcoCiencia & Wildlife Conservation Society, Quito. Address: Fundacion Numashir para la Conservacion de Ecosistemas Amenazados. Mariano Ortiz e Iberia, Ed. Georgina 2, dep. B1, Casilla Postal 17-12-122. Quito, Ecuador, e-mails: jfreile@numashir.org, jachaves@sfsu.edu Appendix List of birds recorded at Otonga (1,700—2,200 m). Threatened, Near Threatened and restricted-range species are emboldened; species only observed en route to the reserve (below 1,800 m) are marked with an *. Species recorded only by Markus P. Tellkamp in April 2002 are marked with a ', and species recorded only by Stewart White er a/. in July-August 2002 are marked with a ”. Coragyps atratus, Cathartes aura, Pandion haliaetus*, Chondrohierax uncinatus*, Elanoides forficatus, Accipiter collaris, Leucopternis princeps, Buteo magnirostris, Oroaetus isidori, Micrastur semitorquatus, Falco sparverius, Aburria aburri, Chamaepetes goudotii, Odontophorus melanonotus, Columba fasciata, Columba plumbea, Geotrygon frenata, Pyrrhura melanura, Bolborhynchus lineola, Pionus sordidus, Piaya cayana, Piaya minuta, Crotophaga ani*, Tapera naevia*, Otus ingens, Glaucidium nubicola, Steatornis caripensis, Nyctibius griseus, Lurocalis rufiventris, Caprimulgus longirostris, Uropsalis lyra, Streptoprocne zonaris, Cypseloides rutilus, Phaethornis syrmatophorus, Doryfera ludovicae, Amazilia tzacatl*, Adelomyia melanogenys, Heliodoxa imperatrix, Heliodoxa rubinoides, Coeligena wilsoni, Coeligena torquata, Boissonneaua flavescens, Heliangelus strophianus, Haplophaedia lugens’, Ocreatus underwoodii, Aglaiocercus coelestis, Pharomachrus auriceps, Trogon personatus, Hapaloptila castanea, Semnornis ramphastinus, Aulacorhynchus haematopygus, Andigena laminirostris, Piculus rivolii, Piculus rubiginosus, Veniliornis fumigatus, Campephilus pollens, Furnarius cinnamomeus*, Synallaxis azarae, Synallaxis unirufa, Cranioleuca erythrops*, Pseudocolaptes boissonneautii, Margarornis squamiger, Premnoplex brunnescens, Premnornis guttuligera, Syndactyla subalaris, Anabacerthia variegaticeps, Thripadectes virgaticeps, Thripadectes ignobilis', Sclerurus mexicanus, Dendrocincla tyrannina, Xiphocolaptes promeropirhynchus, Xiphorhynchus erythropygius, Lepidocolaptes lacrymiger, Campylorhamphus pusillus*, Formicarius rufipectus, Grallaria gigantea, Grallaria alleni, Grallaria ruficapilla, Myornis senilis, Scytalopus vicinior, Scytalopus spillmanni, Juan F Freile & Jaime A. Chaves 16 Bull. B.O.C. 2004 124(1) Pogonotriccus ophthalmicus, Zimmerius chrysops, Mecocerculus poecilocercus, Serpophaga cinerea*, Mionectes striaticollis, Mionectes olivaceus', Pseudotriccus pelzelni, Pseudotriccus ruficeps, Poecilotriccus ruficeps, Myiotriccus ornatus, Myiophobus flavicans, Pyrrhomyias cinnamomea, Contopus fumigatus, Sayornis nigricans, Ochthoeca diadema, Ochthoeca cinnamomeiventris', Myiarchus tuberculifer*, Myiozetetes similis*, Myiodynastes chrysocephalus, Tyrannus melancholicus, Pachyramphus versicolor’, Pipreola riefferii, Lathria cryptolophus?, Rupicola peruviana, Masius chrysopterus, Cyanolyca turcosa, Vireo leucophrys, Myadestes ralloides, Catharus fuscater, Turdus fuscater, Turdus serranus, Cinclus leucocephalus, Progne chalybea*, Notiochelidon cyanoleuca, Stelgidopteryx ruficollis*, Cinnycerthia olivascens, Troglodytes aedon*, Troglodytes solstitialis, Henicorhina leucophrys, Parula pitiayumi*, Dendroica fusca, Geothlypis semiflava*, Myioborus miniatus, Basileuterus tristiatus, Basileuterus coronatus, Conirostrum albifrons, Diglossopis cyanea, Diglossa albilatera, Pipraeidea melanonota, Euphonia xanthogaster, Tangara arthus, Tangara parzudakii, Tangara ruficervix, Tangara nigroviridis, Tangara cyanicollis*, Anisognathus somptuosus, Anisognathus notabilis, Thraupis episcopus*, Thraupis palmarum, Thraupis cyanocephala, Ramphocelus icteronotus*, Piranga leucoptera*, Chlorospingus canigularis**, Chlorospingus semifuscus, Hemispingus melanotis*, Catamblyrhynchus diadema, Pheucticus chrysogaster, Volatinia jacarina’, Sporophila nigricollis, Atlapetes tricolor, Atlapetes leucopterus, Buarremon brunneinucha, Zonotrichia capensis, Carduelis xanthogastra*. Total= 155. © British Ornithologists’ Club 2004 A new subspecies of Sclater’s Monal Lophophorus sclater1 from western Arunachal Pradesh, India by Suresh Kumar R. & Pratap Singh Received 7 January 2003 Sclater’s Monal Lophophorus sclateri T. C. Jerdon, 1870, is one of three species of monal (Phasianidae). It is a restricted-range species occurring within the Eastern Himalayas Endemic Bird Area D08 (ICBP 1992), where it is found in the remote high mountains of Arunachal Pradesh in India, south-east Tibet, northern Myanmar and western Yunnan in China (Ali & Ripley 1983, Smythies 1986, Johnsgard 1986, McGowan & Garson 1995). Sclater’s Monal has remained poorly known and is currently considered Vulnerable (Collar et al. 2001; also Fuller & Garson 2000). Most published information on this species is more than 50 years old and is largely based on natural history notes from Bailey (1916), Beebe (1918-1922), Baker (1919), Kinnear (1934), Ludlow & Kinnear (1937, 1944), Ali & Ripley (1948) and Ludlow (1951). A few recent surveys and studies have produced some information on this species (Kaul & Ahmed 1992, 1993, Kaul et al. 1995, Singh 1994, 1999, Han 2001, Rimlinger et al. 2001). Within Arunachal Pradesh, L. sclateri was thought to occur from 92°-93°E eastwards through the Kameng, Subansiri, Siang and Lohit Districts (Ali & Ripley 1983). However, the confirmed westernmost record for this species is from Mechuka locality in West Siang District, central Arunachal Pradesh (Kaul et al. 1995), east of Suresh Kumar & Pratap Singh 17 Bull. B.O.C. 2004 124(1) 94°E. How far the species extended west and its exact western limit was not known. In the hope of collecting new locality records of this species, and also information on other Galliformes, a survey was conducted in early 1998 in western Arunachal Pradesh. The areas visited were along the Great Himalayan Range and especially in the East Kameng and Lower Subansiri Districts (Fig. 1), which had not been visited previously by biologists. During this survey evidence was obtained of a Sclater’s Monal that differed morphologically from the published descriptions. Discovery of the subspecies In April 1998, while we were surveying the interior parts of Lower Subansiri, a few local tribesmen readily recognized L. sclateri (known locally as thade) from the pictures shown to them. They did, however, insist that the tail of the males was not coloured as in the picture (chestnut with a white subterminal band) but was completely white. Subsequently, SKR came across four completely white rectrices in the irunachal Pradesh eal ey Tibet] Subansain Papumpare Kameng i Lophophorus Impejanus - a Lophophorus sclater? - om Lophophorus sclaten arumachalensis - ASSAM aie ~~ 7 Brenan Figure 1. Map of Arunachal Pradesh showing the distribution of L. s. arunachalensis subsp. nov., along with that of the nominate form and Himalayan Monal. Suresh Kumar & Pratap Singh 18 Bull. B.O.C. 2004 124(1) possession of local people in Damin and Sarli localities in the district. Attached to the rectrices were a few iridescent bluish-green body feathers that were undoubtedly of a monal. The flat, almost square rectrices completely lacked the chestnut coloration of L. sclateri and resembled neither the Himalayan Monal L. impejanus nor the Chinese Monal L. /hyusii, in which the rectrices are cinnamon and iridescent bluish- green respectively. Local people hunt the monal for food and use the tail feathers as a status symbol, and bind the feathers of a complete tail together as a fan. Initially, we thought that the white rectrices might belong to subadults or a morph of L. sclateri, but no ‘normal’ L. sclateri tail feathers were found, and it was considered unlikely that the local people only hunted the monals with white tails. Furthermore, there was no mention of this species having any white tail feathers in the literature. Davison (1974, 1978) proposed an eastern subspecies of Sclater’s Monal L. s. orientalis based on differences in the width of the white subterminal band along the east—west axis of its range. He proposed that in the areas where L. sclateri overlaps with L. impejanus, the former has more white in the tail through character displacement. The white rectrices we collected were from an area where the above two species were thought to meet, but local people there did not recognize L. impejanus and believed that it did not occur in their area. No tail feathers of this species were seen, thereby rendering a character displacement explanation of our white-tailed birds somewhat doubtful. Subsequent observations 10 May 1998. High mountain pass between Sarli and Chayang Tajo, East Kameng District. Tracks and feeding signs, claimed to be of monals by local people, found at 3,400 m but no birds seen. 17 October 1998. Pakdhung camp in the mountains north of Sarli. At 0545 h a male monal seen calling from above the camp in the alpine meadow zone at 4,200 m, with others heard nearby. Between 0600 h and 0930 h, four males and nine females seen and a pair photographed. In the following two days another five females were seen. Back in Sarli a badly damaged and maggot-infested skin of a male and female of the monal were seen with a hunter. 25 October 1999. Wasi camp close to Pakdhung at 3,800 m in the alpine scrub zone. A single male sighted by local assistants and in the following two days a male, female and two subadults were seen between 3,700 m and 3,900 m. At Sarli itself, SKR obtained three skins of the monal (a male, female and immature male) that were in the possession of local people. Another monal skin that appeared to be an immature was also observed with a hunter but could not be obtained. 8 November 1999. In the mountains higher up from Polosung village west of Sarli. One male monal sighted by local assistants at 3,700 m, and the following day a male Suresh Kumar & Pratap Singh 19 Bull. B.O.C. 2004 124(1) Lapiaptorwe eciatert fame phate etiaieri oranachateneis Figure 2.a. The new Sclater’s Monal subspecies Lophophorous sclateri arunachalensis (right) compared with nominate Sclater’s Monal (L. s. sclateri). Oil painting by Debasis Kabasi and R. Suresh Kumar. b. Rectrices of male monals showing indications of possible intergradation with Lophophorus sclateri. Shown on left is the Taksing form, centre L. s. arunachalensis subsp. nov. and right Polosung form. c. The alpine meadow habitat where the new subspecies was found (c.4,100 m). and female monal were spotted by them at 3,800 m. Interestingly, complete rectrices of a male monal from Polosung had a slight chestnut splash along the outer margins of the two outermost feathers, which initially was mistaken for blood stains (Fig.2b). Suresh Kumar & Pratap Singh 20 Bull. B.O.C. 2004 124(1) 12 January 2000. Redding village close to Taksing border post, Upper Subansiri District. A set of rectrices of a male monal was obtained from a hunter that appeared to be a possible intergrade between the white-tailed bird and Sclaters’s Monal: 11 of the 16 feathers had small chestnut spots at the centre of each vane close to the terminal end (Fig.2b). It is not known whether or not these rectrices belong to an immature male of L. s. sclateri. No other rectrices were found showing indications of intergradations or consistent variation according to geographical position. Determination of the subspecies In 2001, SKR examined 38 skins of L. sclateri (Appendix) along with other monal skins in several museums (see Acknowledgements). Only at the Bombay Natural History Society (BNHS) was it possible to compare directly the material collected from white-tailed monals with specimens of L. sclateri. In all other museums a series of photographs was compared with Sclater’s specimens (including the holotype at BMNH). On examination, the white-tailed form was found to resemble L. sclateri in morphology and overall plumage coloration, except for the white tail in the male and the overall darker plumage in the female. Furthermore, plotting the known ranges of the two forms (Fig. 1) revealed that white-tailed birds do not appear to be completely geographically isolated from L. sclateri, as no significant geographical barriers were found. Given the lack of essential evidence on reproductive isolation, in the form of information on vocalizations, behaviour and genetic make-up, we propose the recognition of the white-tailed form as a subspecies of L. sclateri under the Biological Species Concept. Lophophorus sclateri arunachalensis, subsp. nov. Holotype Bombay Natural History Society (BNHS) No. 28946, adult male from Wasi camp close to Pakdhung, Sarli, Lower Subansiri District, Arunachal Pradesh, approx. 28°05’N 93°07’E, India; collected by Suresh Kumar R. from local people who killed the bird for food on 8 November 1999 at 3,800 m in the alpine scrub zone. Paratypes BNHS No. 28948, adult female and BNHS No. 28947, immature male from Wasi camp, Sarli, Lower Subansiri District, Arunachal Pradesh, approx. 28°05’N 93°07°E, India; collected by Suresh Kumar R. from local people who killed the birds for food on 26 October 1999 at 3,750 m in the alpine scrub zone. Diagnosis A large, sexually dichromatic typical monal (Lophophorus) resembling Lophophorus sclateri (Fig. 2a). The presence of curly crown feathers in the male, which is a feature distinctive of L. sclateri, is a clear indication of the relatedness of these two forms. The two other species, L. impejanus and L. lhyusii, differ in size and have a crest of spatulated and elongated feathers respectively, as well as other differences. Both sexes of L. s. arunachalensis are very similar to nominate sclateri Suresh Kumar & Pratap Singh 21 Bull. B.O.C. 2004 124(1) in size (Table 1), bare-part coloration, and plumage pattern and coloration. However, the male differs in having a completely white tail, unlike the chestnut tail with a white subterminal band in nominate sc/ateri. The female differs from nominate sclateri largely in having darker overall plumage with other minor differences. Only one female Sclater’s Monal skin (BMNH: 1938.12.13.454) closely resembles the subspecies in overall coloration, although with minor differences in the tail colour pattern. Description Plumage colour matching was made using Smithe (1975) under natural light. Both the male and female of the subspecies arunachalensis were considered adults based on their plumage and bright coloration of the bare parts. Adult male (holotype). The highly iridescent plumage coloration of the head, neck, back, scapulars and wings, and the velvety black ventral coloration resemble that of nominate sclateri. The only feature that distinguishes the two is the white tail TABLE 1 Comparison of morphometrics [mean + s.d., n (range)] for measurements (mm) of both sexes of Lophophorus sclateri arunachalensis subsp.nov., L. s. sclateri (specimens listed in Appendix), L. Ihuysii and L. impejanus. The mensural data could not be statistically tested due to insufficient sample size (for male and female aruncahalensis is n=1), but measurements of L. s. arunachalensis fall within the range of the nominate form. All measurements except the wing and tail were taken using a vernier calliper. Variable Male Female sclateri __ sclateri lhuysii impejanus _ sclateri __sclateri lhuysii impejanus arunachalensis sclateri arunachalensis sclateri Beak length = - - - - 52.8 488+440,7 56.2+0.0,2 495+23.4, 13 from skull (43.3-53.9) (44.1-55.4) Beak length 33.1 34.221.1,12 485441,10 370225,16 32.9 318222,8 436242,3 34621.3, 14 from skin (32-36.7) (44.0-56.3) (31.4-40.9) (27.5-34.8) (39.3-47.7) (31.9-36.4) omectommemeo ee S12 1-0,12 38:623.7,10 32.0216,16 30.7 28.7+2.0,8 35.842.3,3 2951.0, 14 from nares (29.4-32.1) (29.3-41.4) (29.6-34.5) (25.8-32.0) (34.3-38.4) (27.6-31.1) Wing length 308 308.5+9.9,13 332.9+7.5,13 293.2+69,16 281 2831+9.6,9 315.0+6.1,3 2683+8.2,15 (flattened chord) (297-327) (319-342) (284-310) (269-298) (311-322) (257-284) Tarsus length 76.6 77.121.7,12 80.042.8,12 714+26,17 641 67.74224,9 766434,3 65.6+1.6, 15 (74.3-80.4) (76.7-85.8) (66.9-77.2) (64.2-71.9) (74.6-80.6) (63.1-68.6) Tail length 192 198.3+10.1,12 2714+ 14.8, 13 2143421616 184 168.1+11.3,9 234.3 + 13.3,3 183.1 + 10.1, 15 (181-211) (250-295) (154-243) (149-185) (219-243) (167-203) Beak length from skull—measured from the depression in the forehead (beak and head joint) to tip of the beak. Beak length from nares—measured from the anterior end of the nostril to the tip of the beak. Wing length—measured using a metal scale from the bend at the wrist region to the tip of the longest primary with wing pressed firmly. Tarsus length—measured from the depression in the tarso- metatarsial joint to the end of the tarsus. Suresh Kumar & Pratap Singh 22 Bull. B.O.C. 2004 124(1) coloration in arunachalensis, which is Chestnut (32) with a narrow subterminal white tail-band in the nominate sclateri. In arunachalensis a few feathers in the rump show faint brown central streaks whilst in nominte sclateri the central streaks are faint or dark closest to Dark Grayish Brown (20), in different individuals and in a few birds faint iridescent coloration on the streak is present. In the adult male the orbital skin coloration, when fresh, is bright blue, closest to Spectrum Blue (69); the legs are greenish-yellow; the beak is pale yellow; the iris coloration is not known; and the claws are dusky brown. Adult female (paratype). Overall plumage coloration similar to nominate sclateri except that it is darker. Also differs in the lower back, rump and tail colour pattern. Lower back and rump coloration in arunachalensis is close to Olive Gray (42) but duller, with brown striations closest to Blackish Neutral Gray (82), whilst in nominate sclateri the coloration is dirty greyish-white, close to Smoke Gray (45), with thin wavy brown stripes closest to Olive Brown (28) and with faint cinnamon in a few places. Also the white streaks along the midrib in the rump feathers of arunachalensis is prominent compared to that of nominate sclateri. Tail coloration in the subspecies is closest to Blackish Neutral Gray (82) but darker, with thin irregular white wavy stripes and with very little lateral mottling compared to nominate sc/ateri, where the tail coloration is closest to Fuscous (21) but darker with very pale Cinnamon (39) wavy irregular stripes and with lateral mottling of Cinnamon (39) that appears to occur in distinct bands. The terminal end of the tail in arunachalensis is more broadly tipped with white than in nominate sclateri. In the adult female the orbital skin, when fresh, is bright blue closest to Spectrum Blue (69); the legs are pale greenish- yellow; the beak is pale yellow; the iris brown; and the claws dusky brown. Immature male (paratype). Judged in its first-year (immature) plumage, and although not surgically sexed it was considered a male because a few iridescent bluish-green feathers were observed on the sides of the neck behind the ear-coverts. Overall appearance as in the female, although the brownish-black, closest to Blackish Neutral Grey (82), plumage coloration of the lower throat, breast and some parts of the belly distinguishes it. Also, unlike in the female, the lower back and rump plumage has a white background with prominent wavy terminal barring of dark brown closest to Blackish Neutral Grey (82), followed by finer wavy or mottled markings of the same. The tail is more broadly tipped with white than in the female. The orbital skin is much more extensive than in the female and is dotted with tiny black feathers; part of the forehead is featherless or with tiny black feathers as in the male; the lores have a sparse covering of tiny black feathers and small white feathers. In the immature monal the orbital skin, when fresh, is bright blue closest to Spectrum Blue (69); the legs are pale greenish-yellow; the bill is pale yellow; the iris is brown; and the claws are dusky brown. Ecology and behaviour Distribution L. s. arunachalensis has been seen by SKR only at the type locality in Lower Subansiri, Arunachal Pradesh. However, indirect evidence, in the form of Suresh Kumar & Pratap Singh 23 Bull. B.O.C. 2004 124(1) tail feathers and interviews with local people, indicates that this subspecies occurs elsewhere in Lower Subansiri and in East and West Kameng Districts in the west of the state (Fig. 1), where previously nominate sc/ateri was assumed to occur. The subspecies arunchalensis there is restricted mainly to the high mountains of the main Himalayan Range along the India—China border. Local hunters reported not having seen this monal on the north side of the main range, which is largely dry and unlike the wet forested area in the south. Three major rivers, Kameng, Kurung and Kamala, originate here; the last two are tributaries of the Subansiri. The precise eastern and western distribution limits of arunachalensis are not known. At the eastern end of its range there is a mountain range we call the ‘Subansiri Divide’. This lies close to the Subansiri River that constitutes the district boundary between the Upper and Lower Subansiri Districts and probably acts as a barrier to some extent. The Divide may not, however, be an effective barrier because there are few high ridges. Nonetheless, nominate L. sc/ateri was found to occur only east of this Divide and the new subspecies only to the west, with the possible exception being around the Taksing area close to the Divide where the two may overlap. The western limit of the new subspecies’s range appears to be along the Sela Range, which forms the district boundary between Tawang and West Kameng Districts. The subspecies may overlap here with L. impejanus. Towards the western end, the subspecies is probably rare, as few local people recognised it and those that did reported seeing it only occasionally. In parts of East Kameng and Lower Subansiri Districts, which are the stronghold of the new subspecies, L. impejanus appears to be absent. Habitat At the type locality SKR observed L. s. arunachalensis in the alpine scrub and alpine meadows between 3,800 m and 4,200 m, whilst local assistants reported seeing the monal at 3,700 m in the temperate forests at the edge of the scrub zone. The alpine scrub is characterised by a few species of dwarf rhododendron Rhododendron ciliatum, R. thomsonii, R. kaycei and other unidentified Rhododendron spp., along with fir Abies densa, the last being the dominant tree species here, occurring up to 3,900 m. Also Cassiope fastigiata, and species of Rubus, Berberis and Cotoneaster are present along the treeline and alpine scrub. The ground cover is largely comprised of grass (Agrostis sp.); herbs and low shrubs were in the senescent stage during the survey. Most sightings of the monal in October 1998 were made in these high alpine areas (Fig. 2c). Oak Quercus sp., Rhododendron spp. and maple Acer caudatum dominate the temperate forest and are highly impenetrable because of a dense understorey of hill bamboo Thamnocalamus spathiflorus var. According to local hunters the monals descend from the alpine meadows to the temperate forests, down as far as 3,000 m during the winter. The mountain slopes on the whole are rugged and steep, with sheer drops straight down to the river in some places. Vocalizations The earliest calling male was first heard at 0545 h when it was still twilight. The call was a series of double-noted, moderate- to high-pitched koo(n)iak, Suresh Kumar & Pratap Singh 24 Bull. B.O.C. 2004 124(1) kooo(n)iak, kooooo(n)iak. The first note of the call is more of a whistle, wavering occasionally and ending in a cluck-like note. When flushed, three females and a male made a rapid ki-ki-ki...kivak, kiyak, kiyuk kvuk kvuk in flight and, after alighting on a rock outcrop the male made the double-noted koo(n)iak, kooo(n)iak, kooooo(n)iak call for a while. Differences in vocalizations from nominate sclateri are not known because recordings of the latter were not available for direct comparison. Furthermore, the information available in the literature on the vocalization of Sclater’s Monal is very sketchy. Food The gizzard contents of three female, one immature male and one male arunachalensis collected from a hunter in Sarli, Lower Subansiri District, contained large number of small pebbles, roots, tubers, seeds and bark or leaf parts. The crop contents of a female contained leaves of Potentilla sp., Cardamine sp. and Gaultheria sp. On four occasions the birds were observed digging the ground. We searched for digging or scrape signs from where the birds were flushed. In a few of the dug-over areas there were remains of the underground bulb of the Cobra Lily Arisaema sp. It appeared that the birds fed on the inner fleshy part of the bulb. Local hunters reported using the bulb of Arisaema as bait in snares to trap the monal. Similar dug-over areas and scrape signs were observed at the type locality and at a few other sites. Movements and behaviour At the type locality arunachalensis was found to be extremely shy; the birds flushed at the earliest notice and this was believed to be due to the high level of hunting in the area. However, on one occasion a male was observed calling from a ridgetop whilst three females and a male were feeding quietly further down the slope. On seeing us approach the feeding birds, the male started calling continuously instead of flushing and it only flushed after the birds below left the area. Most females were in flocks of two or three, or with a single male. The female flocks however may have also consisted of subadults, which appear similar to adult females. Males were typically observed singly. A male appeared in the same area from where it had flushed either later in the day or on the next day, and if this was the same individual this may indicate some site-fidelity. Local hunters reported taking advantage of such predictable movements to place snares or set camps from which they could shoot birds. When flushed, the monals glided across or down the slope at great speeds and often to great distances, and on a number of occasions they flew down into the Abies forest in the alpine scrub area. According to local hunters, the monals leave the summer habitat of the alpine meadows and scrub by early October, when they move down to the alpine scrub that lies next to the temperate forest. They may descend even further. Etymology This subspecies is named after the Indian state of Arunachal Pradesh, to which it is probably endemic. Emphasizing the name will further highlight the biological richness of the state, as well as drawing attention to the subspecies’s restricted distribution. Arunachal Pradesh is renowned for its biodiversity and is Suresh Kumar & Pratap Singh 25 Bull. B.O.C. 2004 124(1) listed among the 18 biodiversity hotspots of the world (Myers 1988, 1990). Ten of India’s 17 species of pheasants are found in the state, more than any other. Geographic differentiation As there is no marked difference in morphology and little deviation in plumage coloration from nominate sc/ateri, except for the all- white tail in the male, arunachalensis may not have been isolated long from the nominate form. Furthermore, information presented here on the distribution of the subspecies suggests that it is probably incompletely geographically isolated. Nevertheless, we believe that the Subansiri River, which flows close to the contact zone of the two or the adjacent mountain ridge that forms the district boundary between the Lower and Upper Subansiri districts, may have acted as a partial barrier. It may be relevant that areas along the Himalaya that lie west of 93°E receive more rainfall than areas to the east (Ludlow & Kinnear 1944), and this coincides with the nominate subspecies’s distributional limits, with the new subspecies to the west. Consequently, the difference in rainfall may have had an impact on habitat, and this in turn may have influenced geographic differentiation of the plumage coloration in the subspecies. In the genus Lophophorus, tail feathers play a major role during courtship display, where the tail feathers are held high and fanned out, and slowly flicked up and down (Gaston ef al. 1982, Johnsgard 1986). Selection for conspicuousness of these feathers might have occurred in wetter, lusher vegetation. Conservation L. s. arunachalensis is not currently threatened, because in most parts of its narrow range, especially in the interior, a large proportion of its habitat is so remote as to be intact. The habitat is affected very little by shifting cultivation or slash-and-burn agriculture, as this practice is confined to areas below 2,000 m, far below the subspecies’s altitude range. Although the small geographic extent of the subspecies’s range is of concern, the only current threat is hunting by local people. Even this may be marginal, because larger species such as Takin Budorcas taxicolor and Serow Nemorhaedus sumatraensis are preferred by hunters. The Nishi tribes, living in the East Kameng and Lower Subansiri Districts, consider the monal sacred and have certain taboos against hunting it. In a few areas, however, hunting is extensive and more and more people are using guns, which could possibly lead to local extinctions of the new subspecies. The new subspecies may face some degree of risk as no part of its small range falls under any protected area designation. Moreover, hunting is difficult to curb, as it is a part of the culture of the tribes with which this taxon co-exists. Declaring a large protected area extending from Tawang to Lower Subansiri District, and ensuring that it is effective, is one way of improving the survival prospects of the subspecies, along with other threatened species such as Takin, Musk Deer Moschus chrysogaster and Red Panda Ai/urus fulgens. More surveys to collect information on the exact distribution of the subspecies, and studies especially in the region of contact or overlap with both L. s. sclateri and L. impejanus, should be initiated to clarify the conservation status of the species. Suresh Kumar & Pratap Singh 26 Bull. B.O.C. 2004 124(1) Acknowledgements Many individuals helped us during fieldwork and we thank them all. Special mention must be made of Sape Tani, Sape Takhya, Sape Taza, Milli Tagh, Tatum Tapir and personal assistant Dorji Raptan, who took enormous interest in the work and played an active role in the discovery of the new subspecies. We thank the people of Sarli, Damin, Tali and all other localities visited for their hospitality. We are grateful to P. J. Garson for his constant encouragement and help in organizing funds in short periods of time. We thank V.B. Sawarkar, Director Wildlife Institute of India for infra-structural support. We thank the Arunachal Pradesh State Forest Department for granting permission to carry out the study and forest officials N.S. Bisht, Gapak and C. Loma for their hospitality. Colleagues and friends R. Jayapal, M.V. Nair and K. Black are acknowledged for useful discussions. For access to collections, loans and other assistance in museums, we are grateful to: A. R. Rahmani, N. Chaturvedi and Meghana (Bombay Natural History Society [BNHS], Mumbai, India); P. Rasmussen (National Museum of Natural History [NMNH], Smithsonian Institution, Washington, D.C.); J. Cracraft, P. Sweet and J. Webber (American Museum of Natural History [AMNH], New York); A. Pirie (Museum of Comparative Zoology [MCZ], Harvard); K. Zyskowski (Yale Peabody Museum [YPM], New Haven); D. Willard (Field Museum of Natural History [FMNH], Chicago); C. Voisin (Museum National d’Histoire Naturelle [MNHN], Paris); R. P. Prys-Jones and M. Adams (The Natural History Museum [BMNH], Tring, UK). This study was made possible with financial support from the Wildlife Institute of India (WII), DehraDun, and through the generous support of James Goodhart, member WPA-UK. Funds for museum visits to BNHS, NMNH, AMNH and BMNH by SKR was made possible through support from the WII, NMNH, the Frank Chapman Memorial Fund and J. Goodhart respectively. We thank Nigel Collar and Philip McGowan for discussions and comments, and Edward Dickinson and Geoff Davison for reviewing the manuscript. We thank the Kabasi brothers, of Kolkata, for help in preparing the painting of the monals. References: Ali, S. & Ripley, S. D. 1948. The birds of the Mishmi Hills. J Bombay Nat. Hist. Soc. 48: 1-37. Ali, S. & Ripley, S. D. 1983. Handbook of the birds of India and Pakistan. Oxford Univ. Press, New Delhi. Bailey, F. M. 1916. Notes from southern Tibet. J. Bombay Nat. Hist. Soc. 24: 72-78. Baker, E. C. S. 1919. The game birds of India, Burma and Ceylon. J. Bombay Nat. Hist. Soc. 26: 319- 337: Beebe, W. 1918-1922. A monograph of the pheasants. Reprinted in 1990 by Dover Publications, Inc. New York. Davison, G. W. H. 1974. Geographic variation in Lophophorus sclateri. Bull. Brit. Orn. Cl. 96:163—164. Davison, G. W. H. 1978. Further notes on Lophophorus sclateri. Bull. Brit. Orn. Cl. 98: 116-118. Fuller, R. A. & Garson, P. J. 2000. Pheasants: status survey and conservation action plan 2000-2004. IUCN, Gland, Switzerland & Cambridge, UK and World Pheasant Association, Reading, UK. Gaston, A. J., Lelliot, A. D. & Ridley, M. W. 1982. Display flights of the male Monal pheasant, Lophophorus impejanus. World Pheasant Assoc. J. 7: 90-91 Han Lianxian, 2001. Research on Sclater’s Monal in west Yunnan, China—WPA Progress Report June 1999 to June 2000. Tragopan 13/14: 15-17. ICBP. 1992. Putting biodiversity on the map: priority areas for global conservation. International Council for Bird Preservation, Cambridge, UK. Jerdon, T. C. 1870a. Letter on some new species of birds from the north-east frontier. Jbis (2) 6: 147— 148. Jerdon, T. C. 1870b. Notes on some new species of birds from the north-eastern frontier of India. Proc. Asiatic Soc. Bengal 1870: 59-61. Johnsgard, P. A. 1986. The pheasants of the world. Oxford Univ. Press. Kaul, R. & Ahmed, A. 1992. Pheasant studies in north-east India, Arunachal Pradesh. Unpublished Report. Prepared for the Peter Scott Trust, Jamnagar, India. Kaul, R. & Ahmed, A. 1993. Pheasant surveys in Arunachal Pradesh, India, in February—March 1991. Pp. 50—54 in Jenkins, D. (Ed.). Pheasants in Asia 1992. World Pheasant Association, Reading, UK. Suresh Kumar & Pratap Singh 27 Bull. B.O.C. 2004 124(1) Kaul, R., Raza, R. & Kalsi, R. 1995. Pheasant surveys in Arunachal Pradesh, India. Pp. 28—34 in Jenkins, D. (Ed.). Ann. Rev. World Pheasant Assoc.1993/94. World Pheasant Association, Reading, UK. Kinnear, N. B. 1934. On the birds of the Adung Valley, north-east Burma. J. Bombay Nat. Hist. Soc. 37: 347-368. Ludlow, F. & Kinnear, N. B. 1937. The birds of Bhutan and adjacent territories of Sikkim and Tibet. /bis (14) 1: 1-46, 249-293, 467-504. Ludlow, F. & Kinnear, N. B. 1944. The birds of south-eastern Tibet. /bis 86: 43—86, 176-208, 348-389. Ludlow, F. 1951. The birds of Kongbo and Pome, south-east Tibet. /bis 93: 547-578. McGowan, P. J. K. & Garson, P. J. 1995 Pheasants: status survey and conservation action plan 1995— 1999. IUCN, Gland, Switzerland & Cambridge, UK. Myers, N. 1988. Threatened biotas: “hotspots” in tropical forests. Environmentalist 8: 187-208. Myers, N. 1990. The biodiversity challenge: expanded hot-spots analysis. Environmentalist 10: 243- 256. Rimlinger, D., Bland, J., Xianji, W. & Xiaojun, Y. 2001. Survey for Sclater’s Monal in northwestern Yunnan. 7Jragopan 13/14: 17-19. Singh, P. 1994. Recent bird records from Arunachal Pradesh, India. Forktail 10: 65-104. Singh, P. 1999. Bird survey in selected localities of Arunachal Pradesh, India—March 1997 to July 1998. Unpublished report. Wildlife Institute of India, DehraDun. Smithe, F. B. 1975. Naturalist’s color guide. American Museum of Natural History, New York. Addresses: R. Suresh Kumar, Wildlife Institute of India, Post Box # 18, Chandrabani, DehraDun - 248 001, Uttaranchal, India, e-mail: suresh_wii@yahoo.com (all correspondence should be sent to this address); Pratap Singh, DCF-Wildlife-1, Haddo, Port Blair - 744 102, Andaman and Nicobar Islands, India, e-mail: pratapsingh_birds@rediffmail.com Appendix 1 List of Lophophorus sclateri specimens examined: BNHS 13354: m; collected 1913; Hpinaw, between Kachin Hills & China; F C. Louis. BNHS 13355: f; collected 1913; Hpinaw, between Kachin Hills & China; F. C. Louis. BNHS 13356: f; collected 1914; Htawgaw, between Kachin Hills & China; F. C. Louis. BNHS 13357: m; collected 9.3.1913; Tsu River, Mishmi Hills, Assam (c.2,120 m); Capt. FM. Bailey. BNHS 13358: m; collected 1913; Tsu River, Mishmi Hills, Assam (c.2,120 m); Capt. FM. Bailey. NMNH 328067: m; Delei Valley, Mishmi Hills (¢c.2,425 m), Upper Burma; brought by Mishmis. NMNH 328068: m; collected 4.4.1927; Delei Valley, Mishmi Hills; T.P.M. O’Callaghan. NMNH 608867: m; collected January 1, 1947; Mishmi Hills, N.E. Assam; S.D. Ripley. YPM 42186: f; collected 4.2.1927; Furzz, Delei Valley, Mishmi Hills; brought by Digaru Mishmis. YPM 42187: m; Upper reaches of the Don river, East of Sadiya, Assam, India (c.2,120 m); T.P.M. O’ Callaghan. AMNH 543101: m; collected August 1925; Shweli-Salween Divide, N.W. Yunnan (c.3,330 m, rocky and ravine slopes); G. Forrest. AMNH 543102: Juvenile m; collected September 1925; Shweli-Salween Divide, N.W. Yunnan (c.3,640 m, rocky and ravine slopes); G. Forrest. AMNH 543103: m; collected August 1925; Shweli-Salween Divide, N.W. Yunnan (c.3,330 m, rocky and ravine slopes); G. Forrest. AMNH 543104: m; collected August 1925; Shweli-Salween Divide, N.W. Yunnan (c.3,330 m, rocky and ravine slopes); G. Forrest. AMNH 543105: m; collected September 1925; Shweli- Salween Divide, N.W. Yunnan (c.3,330 m, rocky and ravine slopes); G. Forrest. AMNH 543107: f; collected September 1925; Shweli-Salween Divide, N.W. Yunnan; G. Forrest. AMNH 543108: m; collected 26.5.1913; Yonggyap Latsa (Abor or Mishmi hills, c.3,480 m), Capt. F W. Bailey. MCZ 149255: m; collected August 1925; Shweli-Salween Divide, N.W. Yunnan (c.3,330 m). Forrest. NHM 1871-12-1-1 (Type Specimen): m; died on 12.11.1871 in the Zoological Society’s Gardens, Regents Park, London; collected from Mishmi Hills, Upper Assam; brought by locals to T.C. Jerdon. NHM 1889-5-10-1953: m; collected December 1879; Mishmi Hills, N.E. Assam; Hume Collection (Sir S. Bayley). NHM 1895-7- 14-730:f; collected possibly 1879; Eastern Assam, India; Lt. Col. H.H. Godwin-Austen. NHM 1914-10- 5-1: m; collected 24.3.1913; Tsu River, Mishmi Hills, N.E. Assam (c.2,360 m); Capt. F.M. Bailey. NHM eae een Suresh Kumar & Pratap Singh 28 Bull. B.O.C. 2004 124(1) 1925-5-8-1: f; collected 14.12.1924; Tsangpo Gorge (Po Tsangpo confluence), Tibet (c.2,725 m); F. Kingdon Ward (P). NHM 1925-5-8-2: Immature m; collected 14.12.1924; Po Tsangpo, Tibet (c.2,725 m); F. Kingdon Ward. NHM 1928-7-14-3: m; collected October 1925; Myitkyina district, Upper Burma; Mrs. M. West (P). NHM 1928-7-14-4: m; collected October 1925; Myitkyina district, Upper Burma; Mrs. M. West (P). NHM 1933-11-13-25: m; collected Jan—Feb 1931; Koi Tou Tengyeuh, N.W. Yunnan, China; G. Forrest. NHM 1933-11-13-26: f; collected Jan—Feb 1931; Koi Tou Tengyeuh, N.W. Yunnan; G. Forrest. NHM 1938-12-13-454: f; collected 14.5.1938; Lo La (South) Pachakshiri, S.E. Tibet (c.3,480 m); F Ludlow & G. Sherriff. NHM 1938-12-13-455: m; collected 15.5.1938; Lo La (South) Pachakshiri, S.E. Tibet (c.3,480 m.); EF Ludlow & G. Sherriff. NHM 1938-12-13-456: m; collected 14.5.1938; Lo La (South) Pachakshiri, S.E. Tibet (c.3,480 m); F. Ludlow & G. Sherriff. NHM 1938-12-13-457: m; collected 15.5.1938; Lo La (South) Pachakshiri, S.E. Tibet (c.3,480 m); F. Ludlow & G. Sherriff. NHM 1938-12- 13-463: f; collected 15.5.1938; Lo La (South) Pachakshiri, S.E. Tibet (3,485 m); F Ludlow & G. Sherriff. NHM 1938-12-13-605: m; collected 14.5.1938; Lo La (South) Pachakshiri, S.E. Tibet (c.3,480m); F. Ludlow & G. Sherriff. NHM 1941-12-1-673: m; collected May 1934; 18 miles ENE of Hpinaw, Myitkyina- Yunnan border, Upper Burma (c.3,780—3,940 m); G. W. Whittall. NHM 1948-27-18: m; collected 20.2.1947; Trulung, Po Tsangpo Valley, S.E. Tibet (c. 2,880 m); F. Ludlow (P). NHM 1948-34-1: m; collected 28.3.1948; Chimli Pass, Burma (c.3,180 m); B.E. Smythies (P). NHM 1948-34-2: f; collected 29.3.1948; Chimli Pass, Burma (c.3,180 m); B.E. Smythies (P). © British Ornithologists’ Club 2004 Notes on breeding birds from an Ecuadorian lowland forest Harold F Greeney, Rudolphe A. Gelis & Richard White Received12 February 2003 The lowlands of eastern Ecuador are popular for birdwatching tours as well as ornithological research. Despite this, and the increased interest in the Ecuadorian avifauna in the past 15 years (e.g. Krabbe 1992, Best et al. 1993, Rasmussen et al. 1996, Ridgely & Greenfield 2001), little has been written concerning the breeding biology of birds in the area (but see Greeney 1999, Hill & Greeney 2000, Greeney er al. 2000). As a whole, the natural history, ecology and breeding biology of tropical birds remains poorly understood (Hilty 1994). Here we present data on 32 species, collected over recent years, from two adjacent field sites in the Sucumbios province of eastern Ecuador. Observations were made opportunistically, during the course of other activities, and on their own are not useful for acessing patterns of seasonality. Nonetheless, in conjunction with past and future observations, the data presented here make a significant contribution to our knowledge of birds from this poorly studied area of Ecuador. Sacha Lodge Research Station (SLRS) (00°26’S, 76°27’ W) is located near the community of Afangu, c.65 km east-southeast of Coca along the Napo River at an elevation of 250 m. La Selva Biological Station (LSBS) (00°29’S, 76°22’W) is located only 10 km further downriver from SLRS. Both of these sites are located on Harold F Greeney et al. 29 Bull. B.O.C. 2004 124(1) the north bank of the Napo River, but nests were found on both sides. As the Napo River is thought to be the limit of distribution for some species (Ridgely & Greenfield 2001), the specific side is give with each observation as N (North) or S (South). Nesting records are given in taxonomic order following Ridgely & Greenfield (2001). Species accounts RUFESCENT TIGER-HERON Tigrisoma lineatum 10 March 1998, LSBS (N). The nest, typical of this species, was a loose stick platform located 3 m up in a mangrove tree over the edge of an oxbow lake. Whilst the contents of the nest were not seen, adult behaviour suggests the bird was incubating. Breeding information from Colombia includes breeding condition birds from March to November (Hilty & Brown 1986, Olivares 1974). Stiles & Skutch (1989) described an egg from Suriname and nests have been recorded in Venezuela from July to September (Thomas 1979). BLACK VULTURE Coragyps atratus 1 April 1998, LSBS (N). An adult was found incubating two pale blue eggs with dark brown splotches. The nest was a shallow depression located at the base of a large Ceiba (Bombacaceae) tree, between two large buttressing roots. This species nests from January to May in Panama (Wetmore 1965) and November to February or March in Costa Rica (Stiles & Skutch 1989). Nests with young have been reported from Colombia in April (Hilty & Brown 1986) and at LSBS in June (Hill & Greeney 2000). Whilst this observation, and all the nesting records cited above, reported nests on the ground in similar sheltered positions, Howell & Webb (1995) reported this species breeding communally in tall trees. SLENDER-BILLED KITE Rostrhamus hamatus 25 July 2001, SLRS (N). The nest was located c.25 m up in the outer mid-crown of a large tree in floodplain forest. Both adults were present and vocal around the nest but the contents of the nest were unobservable. Similar nests were described from Suriname (Haverschmidt 1968) and Venezuela (Hilty & Brown 1986, Mader 1981) in July and August to September respectively. DOUBLE-TOOTHED KITE JHarpagus bidentatus 24 April 2001, SLRS (N). On this date an adult bird was first seen building a loose stick platform in the horizontal fork of a Ceiba sp. (Bombacaceae) tree c.35 m above the ground in the swampy clearing in terra firme forest. On 23 August 2001 an adult was seen sitting for long periods on the nest, presumably incubating. During subsequent visits, until 6 September 2001, the birds were continuing to incubate. On one occasion the adult repeatedly called whilst sitting on the nest. The other adult flew in and displaced several Boat-billed Flycatchers Megarhynchus pitangua that were perching in the nest tree. Double-toothed Kites have been reported nesting Harold F Greeney et al. 30 Bull. B.O.C. 2004 124(1) during June in Panama (Laughlin 1952), building during April in Costa Rica (Stiles & Skutch 1989), and in breeding condition from January to April in Colombia (Hilty & Brown 1986, Olivares 1962). ORNATE HAWK-EAGLE Spizaetus ornatus 18 March 2001, SLRS (N). A single nest was found c.30 m above the ground in a Ceiba sp. (Bombacaceae) tree growing in ferra firme forest. The nest was a loosely constructed stick platform c.1 m in diameter. An adult was sitting on the nest at 1200 h and was presumed to be incubating. On 18 April an adult was seen bringing food and at least one nestling could be seen. This species is known to breed from November or December to May in Panama (Brown & Amadon 1968), from March to June in Guatemala (Lyon & Kuhnigk 1985), and from April to May in Costa Rica (Stiles & Skutch 1989). MARBLED WOOD-QUAIL Odontophorus gujanensis 24 December 1997, LSBS (N). One adult was seen inside terra firme forest with at least two dependent chicks. When approached, the chicks quickly nestled into the leaf litter and froze. The adult ran just out of sight and circled around calling continuously. In Colombia, breeding condition birds have been recorded from February to May, a nest with eggs from March, and chicks from April (Blake 1955, Hilty & Brown 1986). In Costa Rica this species breeds from January to August (Skutch 1947, Stiles & Skutch 1989). COLLARED PLOVER Charadrius collaris 15 March 2001, SLRS. A simple scrape nest was found on an island in the Napo River. It was c.20 m from the river edge, c.5 cm deep, and located at the base of a small tuft of grass. There was a single egg. When the nest was approached, the adult engaged in a broken-wing display. This species breeds from March to June in Costa Rica (Stiles & Skutch 1989). Chicks have been reported in January from Venezuela (Friedmann 1948) and a summary of their breeding in Chile was given by Johnson (1965). RUDDY QUAIL-DOVE Geotrygon montana 27 November 2000, SLRS (N). An adult was found incubating two buff-coloured eggs, measuring 24.7 mm x 20.7 mm and 26.3 mm x 20.7 mm respectively. The nest was a loose stick and leaf platform on the top of a 60-cm-high stump in terra firme forest. It measured roughly 19 cm across on the outside, with the 2-cm-deep cup being 8 cm wide. 25 March 2001, SLRS (N). An adult was seen near a nest with two nestlings at 1000 h. The nest was as previously described, located 2 m up in the U of a liana against the side of a large tree in terra firme forest. In Colombia, breeding- condition birds were reported from January to June and a nest with eggs in March (Hilty & Brown 1986, Olivares 1964). Greeney (1999) reported two nests with eggs at LSBS in January. Harold F Greeney et al. 31 Bull. B.O.C. 2004 124(1) COBALT-WINGED PARAKEET Brotogeris cyanoptera 30 April 1998, LSBS (N). A single adult was observed inside terra firme forest excavating a small hole in the side of an arboreal termite (Nasutitermes sp.) nest c.5 m above the ground. 29 July 1998, LSBS (N). A second nest hole, located 6 m up, and also in a termite nest, was seen being entered by a single adult. Nestling begging could be heard but the contents were not seen. Hilty & Brown (1986) reported breeding-condition females in early June from Colombia, but little else seems to have been published on the breeding of this species. COMMON POTOO Nyctibius griseus 2 September 2001, SLRS. A nest was found on a river island c.2.5 m above the ground at the end of a broken Cecropia sp. (Moraceae) stump. At least one nestling was seen. It was sparsely feathered with white down. The breeding of this species is fairly well known (del Hoyo ef al. 1999). RUFOUS-BREASTED HERMIT Glaucis hirsuta 28 July 2001, SLRS (S). Both sexes were seen building a nest attached to the back of an epiphytic fern leaf hanging 1.5 m over a small river. The nest, similar to those of other Phaethorninae, was a small, inverted cone-shaped nest attached with spider webs. This species appears to nest year-round in Colombia (Hilty & Brown 1986) and accounts of breeding behaviour in Colombia have been presented by Todd & Carriker (1922) and Darlington (1931). Snow & Snow (1973) described the breeding of this species in Trinidad. GREAT-BILLED HERMIT Phaethornis malaris 5 August 1998, LSBS (S). An unsexed adult was found incubating two all-white eggs. The nest was an inverted-cone cup fastened to the underside of an understorey palm frond in typical Phaethornis fashion. We have found no other breeding records for this species but the Ecuadorian population has previously been considered a subspecies of Long-tailed Hermit P suwperciliosus (Meyer de Shauensee 1970) and is now considered separate (Hinkelmann 1996, Hinkelmann & Schuchmann 1997). For P. superciliosus, breeding data have been reported from Colombia, Costa Rica and Panama (Hilty & Brown 1986, Skutch 1964, Stiles & Skutch 1989, Wetmore 1968, Willis & Eisenmann 1979). FORK-TAILED WOODNYMPH 7halurania furcata 25 July 2001, SLRS (S). An adult female was flushed from the nest and was found to be incubating two all-white eggs. Subsequently, on 9 August, the nest contained two nestlings and the female was observed brooding. The nest was a small cup located 2.5 m up in an epiphytic fern on a small tree. Little has been published on the breeding of this species, but Hilty & Brown (1986) reported breeding-condition birds from Colombia in June. Harold E Greeney et al. Be Bull. B.O.C. 2004 124(1) BLACK-FRONTED NUNBIRD Monasa nigrifrons 15 August 2001, SLRS (N). One adult was seen excavating a nest cavity c.35 cm up in a c.50-cm-high sandy bank in heavily disturbed flooded forest beside the Napo River. In Colombia, breeding condition birds have been reported in June and a stub- tailed juvenile in November (Hilty & Brown 1986). O’Neill (1974, in Hilty & Brown 1986) reported this species breeding during the dry season in south-eastern Peru. At LSBS this species was previously reported nesting in April (Hill & Greeney 2000). YELLOW-TUFTED WOODPECKER Melanerpes cruentatus 2 April 1998, LSBS (N). Both adults were seen bringing food to nestlings in a cavity inside a dead palm (Mauritia sp.) beside an oxbow lake. Nests and the breeding activity of this species have been described from Peru (Short 1970). Olivares (1962) reported a bird in breeding condition from Colombia in March. ORANGE-FRONTED PLUSHCROWN Metopothrix aurantiacus 27 July 1998, LSBS (N). On this date, at least five individuals were seen following each other into and out of two different nests located in the same tree. A third nest was also located in this same tree. The nests were large bulky balls of sticks, located c.30 m above the ground in open floodplain forest along the Napo River. There is apparently very little known concerning the breeding biology of this species, although the nest was generally described in Ridgely & Greenfield (2001). TAWNY-THROATED LEAFTOSSER Sclerurus mexicanus 1 August 1998, LSBS (N). An adult was seen bringing pale, skeletonised leaves to an excavated hole in the soil surrounding the roots of an upturned tree. The nest burrow was | m up and, beyond a 4-cm tunnel, opened into a cavity roughly 20 cm in diameter. The cavity was lined entirely with skeletonised leaves. This species nests from December to April in Costa Rica (Stiles & Skutch 1989) and breeding condition birds have been reported in Colombia from April and May (Hilty & Brown 1986). The nests described by Stiles & Skutch (1989) from Costa Rica had smaller chambers and longer entrance tunnels than the nest observed here. That described here, however, is similar to the nests of Black-tailed Leaftosser S. caudacutus and Short-billed Leaftosser S. rufigularis, which both nest in burrows built in upturned roots in French Guiana (P.R. Martin, pers. comm.). FASCIATED ANTSHRIKE Cymbilaimus lineatus 26 June 2001, SLRS (N). In an area of flooded forest, both sexes were seen bringing material to a nest located 1.5 m up in a tangle of vines and undergrowth. The nest was fairly unformed at this time. Adults were seen carrying spider silk, bark strips and a small vine with green leaves. Both sexes alternated weaving material into the nest whilst giving muted calls. On 12 July they were still building. On 20 July the male was flushed from the nest and found to be incubating one egg. The egg was white with large brown blotches. At the time of the last observation, on 29 July, the Harold F Greeney et al. 33 Bull. B.O.C. 2004 124(1) male was still incubating a single egg. This species has been reported to breed from April to June in Costa Rica (Stiles & Skutch 1989) and birds in breeding condition were reported in Colombia from March to May (Hilty & Brown 1986). Previous nest descriptions, loosely woven cups of dark fibers, suspended by the their rims in a horizontal fork, resemble the nest found here (Skutch 1972, Stiles & Skutch 1989, Wetmore 1972) and those seen in French Guiana (P.R. Martin pers. comm.). DUSKY-THROATED ANTSHRIKE Thamnomanes ardesiacus 16 August 2001, SLRS (N). At 1445 h, an unsexed adult was flushed from the nest and found to be incubating two eggs. The eggs were pale reddish-cream with even, dark red-brown speckling, except for a distinctly heavier wreath around the larger end. They measured 22 x 16 mm. The nest, at the top of a small hill inside primary forest, was located c.1.75 m up in a small, semi-herbaceous tree (Rubiaceae), suspended between the horizontal petioles of two large leaves. It was an open cup- type nest constructed of dark fibres, leaves and small sticks. The cup was slightly ‘squashed’ and measured 5.5 x 7.0 cm on the inside and 7.0 x 9.0 cm on the outside. The cup was 5.5 cm deep and the nest 9.0 cm tall overall. The nest was visited a total of eight times up to 29 August, when the eggs still had not hatched. Of the occasions when the sex of the incubating adult was determined, the female was seen five times and the male once. On 3 September the nest contained two unfeathered nestlings and on 6 September the chicks were seen to be well covered with down. The nest and eggs described in Hilty & Brown (1986) from Peru appear to match the description given here. WHITE-SHOULDERED ANTBIRD Myrmeciza melanoceps 4 March 1998, LSBS (N). The female was encountered incubating two creamy-buff eggs with red-brown speckling, heaviest at the larger end. They measured 28 x 19 mm and 28 x 18 mm respectively. The nest was a globular ball with a round side entrance and constructed from strips of palm fronds and other dead leaves. Outside dimensions were roughly 16 cm high x 24 cm wide. The entrance was 6 cm high x 9 cm wide with a broad lip extending out 10 cm and 13 cm wide. The nest was located 30 cm above the ground, nestled into the base of a palm seedling in an area of varzea forest, c.750 m from the edge of the Napo River. During subsequent visits to the nest, until 31 March 1998 when the nest was found destroyed, both the male and female were noted to incubate. On one occasion, the male showed a broken-wing display when flushed from the nest. Little is known of the breeding habits for this species but Hilty & Brown (1986) reported breeding-condition birds in June from Colombia. PYGMY ANTWREN Myrmotherula brachyura 26 July 1998 LSBS (N). Both adults were seen building a hanging cup nest c.12 m up in the outer branch of a large tree growing in open floodplain forest. The nest was mostly hidden by the leaves of the tree in which it was constructed. Hilty & Brown Harold FE Greeney et al. 34 Bull. B.O.C. 2004 124(1) (1986) reported a single breeding condition bird in April from Colombia and a nest being built 6 m up in flooded forest in Brazil at the end of August. DWARF TYRANT-MANAKIN Tyranneutes stolzmanni 15 April 2001, SLRS (S). One nestling was discovered in a tiny, sparse black rootlet cup suspended from a horizontal fork 1.5 m up in a small sapling inside terra firme forest. The nest was 5 cm in diameter on the outside with a 3 cm deep x 3.5 cm diameter cup. Previously reported breeding data included breeding condition birds from Colombia in May and March (Olivares 1962, 1964). CHESTNUT-CROWNED BECARD Pachyramphus castaneus 15 March 1998, LSBS (N). Adults were seen entering a nest with food. The ball nest was wedged in the branches of a tall Ceiba sp. (Bombacaceae) tree, c.35 m above the ground. Breeding condition birds and a juvenile were reported from Colombia in May (Olivares 1964) and two similar nests were described from eastern Ecuador in July (Hilty & Brown 1986). WHITE-WINGED BECARD Pachyramphus polycopterus 27 July 1998 LSBS (N). An adult female was seen feeding a juvenile a katydid (Tettigoniidae) in an open floodplain forest along the Napo River. 24 August 2001, SLRS. Both sexes were seen around a globular ball nest c.15 cm diameter. The nest was located in a tree, 8 m above the ground, along the Napo River in an area of second growth. The male was seen going to the nest later that afternoon, but we do not know what stage the nest was in. Breeding condition adults have been recorded from May to August in Colombia, as well as nest-building activity in March and June (Hilty & Brown 1986). Breeding in Costa Rica occurs from April to August (Stiles & Skutch 1989). PINK-THROATED BECARD Platypsaris minor 26 June 2001, SLRS (N). An adult male was observed bringing material to a bulky, suspended, mossy ball nest. The female was nearby and both adults were vocal. The nest was located in primary forest near a recently fallen tree, c.20 m up on a dead snag. 23 August 2001, SLRS. Another nest was observed under construction. Both adults were seen going to the nest and the male was observed carrying soft plant fibres. The nest was being built 10 m above the ground inside the infructescence of an unidentified palm tree in varzea forest. On 3 September the nest was found to be torn down but both adults were in the area. There is apparently little published on any aspect of the breeding ecology of this species. BLACK-TAILED TITYRA Tityra cayana 21 July 2001, SLRS (N). An adult female was seen bringing food to an unknown number of nestlings. The nest was located c.5 m up in the cavity of a dead tree located in an area of cow pasture near the Napo River. In Colombia, breeding Harold F Greeney et al. 35 Bull. B.O.C. 2004 124(1) condition birds have been reported from June and active nests in March, July and November (Hilty & Brown 1986). At LSBS, an active nest was previously reported in March (Hill & Greeney 2000). DOUBLE-BANDED PYGMY-TYRANT Lophotriccus vitiosus 24 August 2001, SLRS (S). An adult was flushed from a nest with two eggs. The eggs were pale buff with sparse brown flecking. The nest was a hanging ball of thin fibres and moss with a side entrance. It was located c.1 m above the ground in a small Piper sp. (Piperaceae) tree, in an area of second growth. Nests were previously reported in September in Suriname and building birds in August from Brazil (Hilty & Brown 1986). YELLOW-BROWED TODY-FLYCATCHER Todirostrum chrysocrotaphum 22 July 1998, LSBS (N). An adult was seen lining a hanging globular nest with soft kapok seed down (Ceiba sp.). The nest was c.35 m up in a large Ceiba sp. tree. 10 September 2000, SLRS. One adult was seen bringing kapok down to a hanging globular ball nest located c.40 m up in the Ceiba sp. tree where the lodge has built a canopy observation tower. 4 April 2001, SLRS (N). Both sexes were seen building a different nest located in the same tree. On 10 April, presumably the same pair had abandoned that nest and begun construction of another on the opposite side of the tree’s crown. The second site chosen was c.1 m away from a paper wasp (Vespidae) nest. This pair constructed until at least 20 April. Then, on 29 May one adult was seen bringing food to the nest. 22 July 2001, SLRS (N). Yet another nest was seen being built in the same tree. This nest was being constructed only 30 cm from the same paper wasp nest. Only one adult was seen building, intermittently pausing to sing. Hilty & Brown (1986) reported a nest in a similar situation from eastern Ecuador in July and a Colombian nest in June was only 4—5 m up in an area of second growth. Proximity to wasp nests was not noted for either of these nests. AMAZONIAN SCRUB FLYCATCHER Sublegatus obscurior 26 July 1998, LSBS (N). Both adults were seen around a nest under construction, but only one was seen to bring material. The nest was an open cup, suspended in the fork of a horizontal branch, c.8 m above the ground in an area of floodplain forest along the Napo River. A stub-tailed juvenile was reported in August and breeding condition birds from January and March in Colombia (Hilty & Brown 1986). Cherrie (1916) reported an active nest in April and ffrench (1973) described the nest and eggs from Trinidad. WHITE-NECKED THRUSH Turdus albicollis 20 March 2001, SLRS (N). An adult was seen incubating two eggs in a cup nest located 2 m up in a small tree. Accounts of Colombian and Trinidad nests can be found in Todd & Carriker (1922) and Snow & Snow (1963). Harold EF Greeney et al. 36 Bull. B.O.C. 2004 124(1) RED-CAPPED CARDINAL Paroaria gularis 24 March 2001, SLRS (N). An adult was seen feeding a fledgling Shiny Cowbird Molothrus bonariensis along a small stream. The fledgling, begging continuously, followed the adult while it fed. On 24 August 2001 at SLRS (N), an open cup nest was found 4 m up in the fork of a small tree in an area of heavy human disturbance. From adult behaviour around the nest, it is presumed that they were incubating, but the nest contents were not seen. On 29 August the nest was found torn apart. Hilty & Brown (1986) reported a male in breeding condition and begging fledglings in June from Colombia. Breeding in Venezuela was reported from June to September (Cherrie 1916, Thomas 1979). Acknowledgements We are all greatly in debt to the staff and management of Sacha Lodge for their help and support during our field studies. Ruth Ann & John V. Moore have generously supported our investigations. Thank you to Rob Dobbs and Paul Martin for reviewing earlier versions of this manuscript. We gratefully acknowledge the ongoing support of the PBNHS for our field studies and natural history work. This is publication number 8 of the Yanayacu Natural History Research Group. References: Best, B. J., Clarke, C. T., Checker, M., Broom, A. L., Thewlis, R.M., Duckworth, W. & McNab, A. 1993. Distributional records, natural history notes, and conservation of some poorly known birds from southwestern Ecuador and northwestern Peru. Bull. Brit. Orn. Cl. 113: 108-119, 234-255. Blake, E. R. 1955. A collection of Colombian game birds. Fieldiana Zool. 37: 9-23. Brown, L. & Amadon, D. 1968. Eagles, hawks, and falcons of the world, vols. 1 and 2. McGraw Hill, New York. Cherrie, G. K. 1916. A contribution to the ornithology of the Orinoco region. Brooklyn Inst. Arts and Sci. Mus. Bull. 2: 133-347. Darlington, P. J., Jr. 1931. Notes on the birds of the Rio Frio (near Santa Marta), Magdalena, Colombia. Bull. Mus. Comp. Zool., Harvard 71: 349-421. del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 1999. Handbook of the birds of the world, vol. 5. Lynx Edicions, Barcelona. ffrench, R. P. 1973. A guide to the birds of Trinidad and Tobago. Livingston Publishing, Wynnewood, PA. Friedmann, H. 1948. Birds collected by the National Geographic Society’s expedition to northern Brazil and southern Venezuela. Proc. U.S. Nat. Mus. 97: 373-569. Greeney, H. F. 1999. Ecuadorian birds: some nesting records and egg descriptions. Avicultural Magazine 105: 127-129. Greeney, H. F., Gordon, C. E., Kaplan, M. E. & Chimera, C. 2000. High occurrence of breeding condition of birds mist-netted in a lowland Ecuadorian rainforest. Avicultural Magazine 106: 10-11. - Haverschmidt, F. 1968. Birds of Surinam. Oliver & Boyd, Edinburgh and London. Hill, R. & Greeney, H. F. 2000. Ecuadorian birds: nesting records and egg descriptions from a lowland rainforest. Avicultural Magazine 106: 49-53. Hilty, S. 1994. Birds of tropical America: a watcher’s introduction to behavior, breeding and diversity. Chapters Publishing Ltd, Shelburne, Vermont. Hilty, S. L. & Brown, W. L. 1986. A guide to the birds of Colombia. Princeton Univ. Press. Hinkelmann, C. 1996. Systematics and geographic variation in Long-tailed Hermit hummingbirds, the Phaethornis superciliosus—malaris—longirostris species group (Trochilidae) with notes on their biogeography. Ornitologia Neotropical 7: 119-148. Hinkelmann, C. & Schuchmann, K. L. 1997. Phylogeny of the hermit hummingbirds (Trochilidae: Phaethornithinae). Studies in Neotropical Fauna and Environment 32:142-163. Harold F Greeney et al. 37 Bull. B.O.C. 2004 124(1) Howell, S. N. G. & Webb, S. 1995. A guide to the birds of Mexico and northern Central America. Oxford Univ. Press. Johnson, A. W. 1965. The birds of Chile and adjacent regions of Argentina, Bolivia and Peru, vol. |. Platt Estab. Graficos, Buenos Aires. Krabbe, N. 1992. Notes on the distribution and natural history of some poorly known Ecuadorian birds. Bull. Brit. Orn. Cl. 112: 168-174. Laughlin, R. M. 1952. A nesting of the Double-toothed Kite in Panama. Condor 54:137-139. Lyon, B. & Kuhnigk, A. 1985. Notes on nesting Ornate Hawk-Eagles in Guatemala. Wilson Bull. 97: 141-147. Mader, W. J. 1981. Notes on nesting raptors in the llanos of Venezuela. Condor 83: 48-51. Meyer de Schauensee, R. 1970. A guide to the birds of South America. Livingston Publishing, Wynnewood, PA. Olivares, A. 1962. Aves de la region sur de la Sierra de la Macarena, Meta, Colombia. Rev. Acad. Colombiana Ciencias Exactas, Fisicas, Naturales 11: 305-344. Olivares, A. 1964. Adiciones a las aves de la Comisaria del Vaupés (Colombia), II. Caldasia 9: 150-84. Olivares, A. 1974. Aves de la Orinoquia Colombiana. Inst. Cienc. Nat. Ornithologia Univ. Nac. Colombia. Rasmussen, J. F., Rahbek, C., Poulsen, B. O., Poulsen, M. K. & Bloch, H. 1996. Distributional records and natural history notes on threatened and little known birds of southern Ecuador. Bull. Brit. Orn. Cl. 116: 26-45. Ridgely, R. S. & Greenfield, P. J. 2001. The birds of Ecuador. Cornell Univ. Press, Ithaca, New York. Short, L. L. 1970. Notes on the habits of some Argentine and Peruvian woodpeckers. Amer. Mus. Novit. 2413: 1-37. Skutch, A. F. 1947. Life history of the Marbled Wood-Quail. Condor 49: 217-232. Skutch, A. F. 1964. Life histories of Hermit Hummingbirds. Auk 81: 5-25. Skutch, A. F. 1972. Studies of tropical American birds. Publ. Nuttall Orn. Cl. No. 10, Cambridge Mass. Snow, D. W. & Snow, B. K. 1963. Breeding and annual cycle of three Trinidad thrushes. Wilson Bull. 75: 27-Al. Snow, D. W. & Snow, B. K. 1973. The breeding of the Hairy Hermit (Glaucus hirsuta) in Trinidad. Ardea 61: 106-122. Stiles, F. G. & Skutch, A. F. 1989. 4 guide to the birds of Costa Rica. Cornell University Press, Ithaca, New York. Thomas, B. T. 1979. The birds of a ranch in the Venezuelan llanos. Pp. 213-232 in Eisenberg, J.F. (ed.) Vertebrate ecology of the northern Neotropics. Smithsonian Institution Press, Washington D.C. Todd, W. E. C. & Carriker, M. A. Jr. 1922. The birds of the Santa Marta region of Colombia: a study in altitudinal distribution. Ann. Carnegie Mus., vol. 14. Wetmore, A. 1965. Birds of the Republic of Panama. Part 1. Tinamidae (Tinamous) to Rynchopidae (Skimmers). Smithsonian Institution Press, Washington, D.C. Wetmore, A. 1968. Birds of the Republic of Panama. Part 2. Columbidae (Pigeons) to Picidae (Woodpeckers). Smithsonian Institution Press, Washington, D.C. Wetmore, A. 1972. Birds of the Republic of Panama. Part 3. Dendrocolaptidae (Woodcreepers) to Oxyruncidae (Sharpbills). Smithsonian Institution Press, Washington, D.C. Willis, E. O. & Eisenmann, E. 1979. A revised list of birds of Barro Colorado Island, Panama. Smithsonian Contrib. Zool. 291: 1-31. Addresses: Harold F. Greeney, Yanayacu Biological Station & Center for Creative Studies, Cosanga, Napo, Ecuador, c/o 721 Foch y Amazonas, Quito, Ecuador, e-mail: yanayacul@hotmail.com. Rudolphe A. Gelis and Richard White, Sacha Lodge Research Station, Anangu, Sucumbios, Ecuador, c/o Julio Zaldumbide 375 y Toledo, Quito, Ecuador. © British Ornithologists’ Club 2004 Ralf Strewe & Cristobal Navarro 38 Bull. B.O.C. 2004 124(1) New and noteworthy records of birds from the Sierra Nevada de Santa Marta region, north-eastern Colombia by Ralf Strewe & Cristobal Navarro Received 17 March 2003 The Sierra Nevada de Santa Marta is an isolated pyramid-shaped massif on the Caribbean coast of north-east Colombia close to the border with Venezuela. The twin snow-covered peaks, Pico Simon Bolivar and Pico Cristobal, reaching an altitude of 5,775 m just 46 km from the Caribbean coast, represent the world’s highest coastal massif. Because of its altitudinal variation as well as its location, the region contains a mosaic of globally significant biomes (nearly all those to be found in tropical America) from mangroves, semi-deserts, tropical dry forests and tropical wet forests, montane forests and paramos; the region is unique for its small size (c.11,000 km”) combined with its large variety of habitats. Recent studies by the authors during July 1999 to January 2003 on the biogeography and conservation of the avifauna within the Sierra Nevada de Santa Marta Endemic Bird Area (EBA 036) (Stattersfield et a/. 1998) and the adjacent lowlands, including the Ciénaga Grande wetlands, has yielded noteworthy distributional records of 20 bird species, with one species new to Colombia, new registrations for the Caribbean and Sierra Nevada region, and noteworthy altitude extensions for 26 bird species. All 20 bird species with new distributional records were not recorded by Todd & Carriker (1922), who amassed intensive ornithological collections at the beginning of the 20th century over a period of several years and at different sites and elevations within the Sierra Nevada area. Following the latter study no other intensive investigations took place. and information on the avifauna of the Sierra Nevada was principally collected along the San Lorenzo Ridge in the vicinity of Santa Marta city. Much of the information included in this paper results from avifaunal surveys within the study areas of the San Salvador Valley and Toribio Valley on the northern slope of the massif, concentrated at elevations below 2.000 m. The Toribio Valley (localities Haciendas E] Recuerdo, Cincinati, Vista Nieve) encompasses humid montane and premontane forest. and tropical humid forest, in the lower valley. Below 500 m very little forest persists, as the land is intensively farmed and used for cattle grazing. At 500—1.800 m, the valley represents a mosaic of humid premontane forest fragments, shade-coffee plantations and pasture. Above 1,800 m still-larger forest fragments exist up to the San Lorenz ridge. The San Salvador Valley is characterized by extensive primary forests along an altitudinal gradient of 600 to 2.300 m, and isolated forest patches and secondary forest at elevations from sea level to 600 m (Strewe in press, a). Additionally, excursions were made Ralf Strewe & Cristobal Navarro 39 Bull. B.O.C. 2004 124(1) to the western and southern slopes of the massif and to the National Parks Tayrona and Isla de Salamanca within the coastal region, where boreal migratory bird species in particular were monitored. Data were collected during fieldwork within the project ‘Habitat conservation of migratory and resident bird species in the Sierra Nevada de Santa Marta’, conducted in 2000-2003 (Salazar & Strewe unpubl.). Study areas were visited monthly during excursions of 5—10 days. Bird populations were monitored using standardised methodologies for assessing bird population abundance (mist-netting [15x12 m], fixed-radius point counts, non-systematic field observations and tape-recordings). Birds were measured, photographed and selectively marked with colour rings. Tape- recordings, using a Sony TCM 5000 EV and Sennheiser ME66 microphone, were made on most days; copies of recordings have been deposited at Banco de Sonidos Animales (BSA), Alexander von Humboldt Institute, Bogota. The majority of records included herein were obtained at ten localities (Fig. 1): (1) San Salvador Valley, located on the northern slope of the Sierra Nevada de Santa Marta, department of La Guajira (11°05’N, 73°35’ W; 8,400 ha), including Buena Vista nature reserve (450 ha), which protects premontane forest at 600— 2,300 m (Strewe in press, a). (2) El Recuerdo (11°07’N, 74°06’), Cincinati (11°06’N, 74°05’W) and (3) Vista Nieve (11°05’N, 74°05’W), three private coffee farms in the foothills of the San Lorenzo ridge within the Toribio Valley (600-—1,900 m), including wet premontane forest and shade-coffee plantations. (4) San Lorenzo ridge (11°45’N, 78°58’W) in the vicinity of Santa Marta city includes wet premontane and montane forest at 1,800 to 2,800 m; primary forest still exists on the slopes of the ridge, whilst secondary forest and pine plantations dominate in the vicinity of the National Park Unit station and the military base. (5) Tayrona National Park (11°18’N, 73°56’W), protecting c.15,000 ha of mangroves, dry tropical to humid tropical forest at sea level to 600 m. The park area includes disturbed and secondary habitats in the lower and plain sectors, and primary forest on the slopes and ridges. (6) Los Besotes (10°31’N, 72°16’E), private nature reserve (450 ha), first-designated Colombian Important Bird Area (IBA) on the southern slope of the Sierra Nevada de Santa Marta, department Cesar c. 20 km north-east of the capital Valledupar, protecting primary forest at 300—2,000 m. (7) El Congo (10°59’N, 74°04’ W), nature reserve of Fundacion Pro-Sierra Nevada (40 ha) on the western slope of the Sierra Nevada mountains protecting premontane forest at 600—1,050 m. At 500—1,800 m, the valley represents a mosaic of humid premontane forest fragments, shade-coffee plantations and pasture; above 1,800 m still-larger forest fragments exist (Strewe in press, b). (8) Filo Cartagena (11°06’N, 73°69’W; 850 m) and (9) Alto de Mira (11°05’N, 73°56’ W; 950 m), ecological stations at the limits of the Sierra Nevada de Santa Marta National Park within premontane forest. Primary forest around these Ralf Strewe & Cristobal Navarro 40 Bull. B.O.C. 2004 124(1) Mar Caribe Figure 1. Map showing the geographical locations of the Sierra Nevada de Santa Marta region. (1) Buena Vista nature reserve, San Salvador Valley, (2) El Recuerdo, (3) Vista Nieve, (4) San Lorenzo, (5) Tayrona National Park, (6) Los Besotes nature reserve, (7) El Congo nature reserve, (8) Filo Cartagena, (9) Alto de Mira, (10) Isla de Salamanca. stations was visited only a few times, because of problems with working permits from indigenous communities in the area. (10) Isla de Salamanca (10°59’, 74°32’ W) National Park (54,000 ha), limited in the west by the Magdalena river, the Caribbean Sea in the north and the Ciénaga Grande de Santa Marta, Colombia’s largest lagoon and Biosphere and RAMSAR reserve, in the south. The National Park is protecting coastal lagoons and nearly undisturbed mangroves. Species accounts GREY TINAMOU Tinamus tao This tinamou is rare and local in humid forest, principally in foothills; known from the Perija Mountains and the upper Cesar Valley near Fonseca (Hilty 2002, Hilty & Brown 1986), where heavy destruction of the natural habitats has occurred (pers. Ralf Strewe & Cristobal Navarro 41 Bull. B.O.C. 2004 124(1) obs.). Individuals were heard at 2,100 and 2,400 m at San Lorenzo ridge in January 2003 (tape-recording), representing an altitudinal extension from 1,900 m (Hilty 2002, Hilty & Brown 1986). P. Coopmans registered the species at the same locality (in litt.). BARE-THROATED TIGER-HERON Tigrisoma mexicanum Known in Colombia from the extreme north-west in the lower Atrato and the Gulf of Uraba region (Hilty & Brown 1986). The observation of an adult (photo) at a mangrove border at Los Cocos, Isla de Salamanca National Park, on 15 October 2002, signifies a range extension of 410 km north-west. SWALLOW-TAILED KITE Elanoides forficatus The species is distributed throughout Colombia, except the dry Caribbean region from department Atlantico eastward (Hilty & Brown 1986). Within the study area individuals or small groups were recorded frequently across study sites from the period March to May, which may indicate that these were transients from Central America (Ferguson-Lees & Christie 2001, Hilty 2002, Hilty & Brown 1986). BLACK-AND-WHITE HAWK-EAGLE Spizastur melanoleucos This little-known raptor is patchily distributed across Colombia with only a handful of records in humid and wet forest. The closest geographical records are 150 km distant on the western slope of Serrania de Perija and Rio Cesar valley (departments of Guajira and Cesar), with a recent record from the Serrania de San Lucas (Hilty & Brown 1986, Salaman et a/. 2002). The species was discovered for the Sierra Nevada region within the upper San Salvador Valley. Observations of individuals within the Buena Vista nature reserve occurred on 8 July 2000, with an adult perching in an open canopy of premontane forest at 450 m, on 19 September 2000, an adult soaring at 1,200 m, and on 18 April 2001, with close views of an adult soaring over primary premontane forest at 800 m. AMERICAN GOLDEN PLOVER Pluvialis dominica An uncommon transient in Venezuela and Colombia with few spring records, at Buenaventura Bay in February 1984 and in April 1977 east Vichada (Hilty & Brown 1986, Hilty 2002). On 8 April 2001 three individuals were observed migrating north along a ridge at 3,800 m within the upper rio Frio Valley. PEARLY-BREASTED CUCKOO Coccyzus euleri The species is distributed very locally in sandy-belt woodland, scrub and gallery forest in Suriname, Guyana, south-east Peru, east and south Brazil, and northern Argentina. It is known from one record on the Caribbean coast near Cartagena in January (del Hoyo et al. 1997, Hilty & Brown 1986). The new records for the study area come from the Tayrona National Park, sector Neguanje, in tropical dry forest, where an adult was observed at close range for several minutes on | May 1997, and Ralf Strewe & Cristobal Navarro 42 Bull. B.O.C. 2004 124(1) 230 km from Cartagena, in the southern foothills of the Sierra Nevada Mountains, at 300 m within the Los Besotes nature reserve, where another adult was found in tropical dry forest on 23 May 2001 (observation with Bernabé Lopez-Lanus). The status and even the general distribution of this scarce cuckoo remain very poorly understood. MANGROVE CUCKOO Coccyzus minor This rare cuckoo is known from ‘Bogota’ skins presumably from Colombia (Hilty & Brown 1986). In Venezuela the species is rare, with two specimens from Capure, northern Delta Amacuro (1966) and additional observations exist in Red Mangroves Rhizophora mangle at Caio Macareo, Delta Amacuro and from Islas Los Roques in June 1988 (del Hoyo etal. 1997, Hilty 2002). On 21 November 2002 two individuals were observed along the Santa Marta—Barranquilla road at a mangrove border within the Isla de Salamanca National Park (photo). Both individuals stayed low in Red Mangroves and vocalized a very nasal aan aan aan aan aan urmm urmm, slightly accelerating, with the last two notes lower and longer (per Sibley 2001). COMMON POTOO Nyctibius griseus The species is distributed patchily throughout Colombia, but without definite records from Santa Marta and the arid Caribbean region (del Hoyo et al. 1997, Hilty & Brown 1986). The first registrations for the Santa Marta region come from the Caribbean plain with a nest reported by locals at Casa Loma nature reserve, in April 1999, individuals calling at San Salvador Valley (250 m) on 10 March 2000, and at Vista Nieve (1,000 m) on 30 January 2003 (tape-recording). CHESTNUT-COLLARED SWIFT Cypseloides rutilus Known from all three Cordilleras and Serrania de San Lucas, but unrecorded in the Santa Marta or Perijaé Mountains (Hilty 2002, Hilty & Brown 1986). Within the study area the species is not uncommon, with 22 registrations at elevations from sea level, at Rodadero, to 3,200 m in the rio Frio Valley (altitudinal range extension from 600 m for Colombia; del Hoyo et al. 1999 mention records down to sea level). Additional records were of groups with up to 30 individuals from the San Lorenzo ridge at 2,800 m (tape-recording), from Cincinati and Vista Nieve (1,200 m), from the San Salvador Valley (100-800 m) and from El Congo on the western slope Figure 2 (on opposite page). Some examples of poorly known and rarely photographed birds from north-east Colombia. a. Male Lazuline Sabrewing Campylopterus falcatus (Ralf Strewe) b. Male Scaled Piculet Picumnus squamulatus (Ralf Strewe) c. Ruddy Woodcreeper Dendrocincla homochroa (Ralf Strewe) d. Zeledon’s Tyrannulet Phyllomyias zeledoni (Ralf Strewe) e. Male Coppery Emerald Chlorostilbon russatus (Ralf Strewe) f. Female Rosy Thrush-tanager Rhodinocichla rosea (Ralf Strewe) Ralf Strewe & Cristobal Navarro ; Bull. B.O.C. 2004 124(1) Ralf Strewe & Cristobal Navarro 44 Bull. B.O.C. 2004 124(1) (1,000 m). In June 2001 the presence of this species in Perijé Mountains was also confirmed at Cerro Pintado, La Guajira (pers. obs.). GREY-RUMPED SWIFT Chaetura cinereiventris Records for this species in northern Colombia are from the northern foothills of the West and Central Andes, in Antioquia and recently from both flanks of the Serrania de San Lucas (Hilty & Brown 1986, Salaman ef a/. 2002). An adult was caught at 850 m at Filo Cartagena on the northern slope in October 2000 (photo), representing the first record for the Caribbean region and Sierra Nevada Mountains. Additionally, the species was observed at El Congo with two individuals on 29 November 2000, in the rio Frio Valley at 1,400 m in April 2001 and three times at El Recuerdo in September and October 2002. LESSER SWALLOW-TAILED SWIFT Panyptila cayenensis This swift is little known in Colombia with only one previous Central Cordillera record in Caldas, in the mid-Magdalena valley, and a pair observed in the Serrania de San Lucas in March 2001 (Hilty & Brown 1986, Salaman ef al. 2002). In Venezuela the species is recorded below 1,000 m at the base of both slopes of the Andes in Tachira and Mérida, but not from the Perija Mountains (Hilty 2002). New distributional records of the species come from the Tayrona National Park, at Calabazo (150 m) in January 2001, from El Recuerdo (800 m), from Vista Nieve (1,300 m) with four individuals in November 2002 (tape-recording), from Filo Cartagena (850 m) with ten individuals in October 2000, and from the San Salvador Valley (600 m), where a group of 22 individuals was registered in November 2000 and three nests found in December 2002 (photo). These nests were at 8—15 m from the ground on heavy tree trunks at forest borders or within natural clearings (elevations 400—700 m). LAZULINE SABREWING Campylopterus falcatus The species is distributed locally and uncommonly in humid forest, forest borders and shady plantations on both slopes of the East Andes, including the Perija Mountains as the nearest population to the study area (Hilty & Brown 1986, Hilty 2002), where during an excursion to the Cerro Pintado (department of Cesar), two leks at 1,800 and 2,200 m were found in primary montane forest in June 2001 (tape-recording). New registrations for the study area come from four different sites on the northern slope of the Sierra Nevada, spanning the whole study period. Twenty-three individuals were caught, including males (Fig. 2a), females and juveniles between 450 to 1,200 m in the San Salvador Valley, at Filo Cartagena (800 m) in October 2000, at El Recuerdo (800 m) and at Vista Nieve (1,600 m) in July and October 2002. An active lek of five males was recorded at Vista Nieve within premontane forest at 1,300 m in June 2002. This lek is close to a main trail at a distance of only 1.2 km from the cabin, Ralf Strewe & Cristobal Navarro 45 Bull. B.O.C. 2004 124(1) where the collector M.A. Carriker lived and collected intensively in previous years (Todd & Carriker 1922). It is highly unlikely that he would have failed to encounter the lek of this species so close to his home. The recent records of the species are very interesting and raise the question, how and when did the species reach the northern slope of the Sierra Nevada massif from its original distribution on the west slope of the Perija Mountains, where most of the species’ habitats have been destroyed (pers. obs. June 2001). SCALED PICULET Picumnus squamulatus The species is known from the base of the Sierra de Perija in Venezuela, but is not recorded from the base of the same mountains in Colombia. An isolated record exists from the south end of the Santa Marta range (Hilty 2002, Hilty & Brown 1986). Within the study period the species was observed several times in shade- coffee plantations at 1,100 m at Vista Nieve, and once at a forest border at 900 m at El Congo on the western slope. Captures were made at El Recuerdo (800 m), with an adult male on 26 September 2002 (Fig. 2b), and from Alto de Mira, with a female in January 1995 (M. Alvarez in Jitt.). The captured adult male, and also adult males seen in the field, showed yellow forecrown spots. Males of the race roehli, recorded from the southern slope of the Santa Marta range and north Venezuela, have red forecrown spots, sometimes yellow or orange. The race /ovejoyi (extreme north- west Venezuela, department Zuila) is similar, but the forecrown spots of males are always yellow instead of red (del Hoyo ef al. 2002). Following del Hoyo et al. (2002) the individuals from the northern slope of the Sierra Nevada Mountains are of the Jovejoyi type, as all males showed clear yellow forecrown spots and greyer upperparts, representing the first records of this subspecies in Colombia. RUDDY WOODCREEPER Dendrocincla homochroa Only few Colombian records exist of this rare treehunter, including from both slopes of the Perija Mountains and two records from humid forest in foothills on the east slope of the Santa Marta range in the department of Guajira (La Cueva, Los Gorros) (Hilty 2002, Hilty & Brown 1986). The species is common on the northern and north-western slope of the massif, with a total of 57 individuals caught in the San Salvador Valley (250-650 m), Alto de Mira (1,200 m) in December 1995 (Alvarez in litt.), El Recuerdo (800 m) and Vista Nieve at 1,600 m (Fig. 2c). This represents an altitudinal range extension from 1,250 m (Hilty 2002, Stotz et al. 1996), and range extension across the entire massif (85 km). The species is an indicator for premontane forest in good condition, as it was never registered in disturbed or secondary forest within the study area. Hilty (2002) noted that the species was fairly common formerly, but is declining because of forest clearance within its small Venezuelan range. Knowledge of its limited distribution is important given that it is vulnerable to premontane forest destruction in northern Colombia. Ralf Strewe & Cristobal Navarro 46 Bull. B.O.C. 2004 124(1) ZELEDON’S TYRANNULET Phyllomyias zeledoni The species is very uncommon and locally distributed between 470 to 1,800 m in Venezuela, including the Sierra de Perija (1,640 m), on Cerro Pejochaina. In Colombia few records exist in humid foothill forest in Meta and in west Caqueta (Hilty 2002, Hilty & Brown 1986). The first record for northern Colombia comes from El Recuerdo (800 m), where an adult was caught at a forest border on 18 October 2002 (Fig. 2d). The individual had light reddish-brown eyes, a pinkish-orange bill below, the typical greyish crown of the subspecies wetmorei, two narrow pale yellowish wingbars, a sharp white eyebrow, the chest flammulated yellowish olive and very characteristic Spiny tarsi. PINE WARBLER Dendroica pinus The first record for Colombia and South America comes from Vista Nieve (Curson et al. 1994, Rodner et al. 2000), where a first-year female was observed intensively by the authors and S. Restrepo at 1,050 m on 20 November 2002. The individual was studied using the Sibley (2001) guide over 10 minutes in optimal light and at a distance of less than 15 m, showing a pale neck patch, dark cheeks, white spectacles, blurry streaks on the sides of the breast, white undertail-coverts and a long tail projection. The bird was feeding in the low canopy of an /nga tree (8 m) within a shade-coffee plantation, following a mixed-species flock, including Blackburnian Warbler Dendroica fusca and Tennessee Warbler Vermivora peregrina. YELLOW-THROATED WARBLER Dendroica dominica The species is known in South America from a sighting at Barranquilla in December 1969 and at Guiara Wash, south of Santa Marta, in October 1971 (Hilty & Brown 1986). The third record for South America is from the San Lorenzo ridge, where an adult male was observed at the border of an exotic pine plantation at 2,200 m on 20 February 2003. The species was accompanying a flock of resident species, together with Blackburnian Warbler and Tennessee Warbler. The observation was made in good light and at close distance (identification made using Sibley 2001). CHESTNUT-SIDED WARBLER Dendroica pensylvanica Three Colombian records exist for this warbler, from Tolima (October), Santander (November) and south of Cali in the Cauca Valley (November) (Hilty & Brown 1986). New records for the Caribbean region come from the San Salvador Valley, where an adult male was observed at a forest border (150 m) on 3 February 2001 and an adult female at 250 m on 17 March 2001. During an excursion to the adjacent Palomino River Valley another female was encountered in the canopy of a flowering Anacardium tree at 50 m on 22 February 2001. Other observations of singletons come from Tayrona National Park (eastern side) and along the Santa Marta- Ciénaga road in October 1994 (Paul Salaman in /itt.) Ralf Strewe & Cristobal Navarro 47 Bull. B.O.C. 2004 124(1) FULVOUS-HEADED TANAGER 7hlypopsis fulviceps The species is known in Colombia from the Sierra de Perija (to 1,900 m in June 2001, pers obs.) and from the Eastern Cordillera in Norte de Santander (Hilty & Brown 1986, Isler & Isler 1999). In Venezuela the species is uncommon at 800— 1,900 m in the Sierra de Perija (subspecies obscuriceps) (Hilty 2002). On 19 April 2001 two individuals were observed accompanying mixed-species flocks at 2,050 m and 2,380 m at premontane forest borders within the upper rio Frio Valley, on the western slope of the Sierra Nevada massif (photo), representing a 120-km range extension. SOOTY GRASSQUIT Tiaris fuliginosa Known in Colombia from the upper Magdalena and upper rio Patia valleys (Hilty & Brown 1986). In Venezuela it is recorded between 800—1,700 m in the Sierra de Perija, where it is apparently local or seasonal in dry grassy scrub, along borders of moist and humid woodland or at grassy openings in lighter woodland (Hilty 2002). Within the study area, in total 62 individuals (males, females and juveniles) were caught at different localities, at Alto de Mira (M. Alvarez in Jitt.), within the San Salvador Valley at 250 and 450 m, El Recuerdo (800 m), Vista Nieve (1,600 m), and El Congo (850 m), representing a significant range extension and the first recording of the zuliae subspecies for Colombia. A nest was found at El Congo in January 2002 (photo). Additional significant altitudinal extensions Noteworthy altitude extensions registered during the study period are listed for 26 bird species below; the maximum or minimum elevation for each species, based on data in Fjeldsa & Krabbe (1990), Hilty (2002), Hilty & Brown (1986), Renjifo et al. (2002), Ridgely & Greenfield (2001) and other recent publications, is followed by the new altitude extension and the locality. SEMICOLLARED HAWK Accipiter collaris in Andes to 2,200 m (Ferguson-Lees & Christie 2001), from 1,800 m to 2,400 m at San Lorenzo ridge. ZONE-TAILED HAWK Buteo albonotatus in Venezuela to 600 m (Hilty 2002), from 500 m to 800 m in San Salvador Valley. BAND-TAILED GUAN Penelope argyrotis in Venezuela in Coastal Cordillera down to 300 m (Hilty 2002), from 900 m down to 350 m in San Salvador Valley. BLACK-FRONTED WOOD-QUAIL Odontophorus atrifrons in Venezuela at 1,650—3,100 m (Hilty 2002), from 1,200 m to 700 m at El Congo. SANTA MARTA PARAKEET Pyrrhura viridicata from 2,000 m (Hilty & Brown 1986) to 3,200 m at rio Frio. Ralf Strewe & Cristobal Navarro 48 Bull. B.O.C. 2004 124(1) COPPERY EMERALD Chilorstilbon russatus at 500 m (del Hoyo et al. 1999) down to 250 m at Cerro Boliche, Santa Marta (Fig. 2e). WHITE-TAILED STARFRONTLET Coeligena phalerata from 1,400 m (del Hoyo et al. 1999) down to 1,200 m in the San Salvador Valley. SANTA MARTA WOODSTAR Chaetocercus astreans from 825 m (del Hoyo et al. 1999) down to 350 m in the San Salvador Valley. YELLOW-BILLED TOUCANET Aulacorhynchus calorhynchus in Venezuela down to 900 m (Hilty 2002), from 600 m down to 350 m in the San Salvador Valley. KEEL-BILLED TOUCAN Ramphastos sulfuratus from 1,600 m (del Hoyo et al. 2002) to 1,900 m at San Lorenzo. COCOA WOODCREEPER Xiphorhynchus susurrans down to 1,800 m in Venezuela (Hilty 2002), from 1,100 m to 1,600 m at Vista Nieve. STREAK-CAPPED SPINETAIL Cranioleuca hellmayri from 1,600 m (Stattersfield et al. 1998) down to 1,200 m in the San Salvador Valley. MONTANE FOLIAGE-GLEANER Anabacerthia striaticollis 900—2,300 m in Venezuela (Hilty 2002), from 1,000 m down to 600 m in the San Salvador Valley. SANTA MARTA WHITE-CROWNED TAPACULO Scytalopus sanctaemartae from 1,350 m (Stattersfield et al. 1998) down to 600 m in the San Salvador Valley. BROWN-RUMPED TAPACULO Scytalopus latebricola from 2,150 m (Stotz et al. 1996) down to 1,900 m on the San Lorenzo ridge. GOLDEN-BREASTED FRUITEATER Pipreola aureopectus down to 800 m in the Coastal Cordillera in Venezuela (Hilty 2002), from 1,300 m down to 600 m in the San Salvador Valley. MOUNTAIN ELAENIA Elaenia frantzii down to 1,200 m in Venezuela (Hilty 2002), from 900 m down to 600 m in the San Salvador Valley. BLACK-CHESTED JAY Cyanocorax affinis to 1,700 m in Venezuela (Hilty 2002), from 2,200 m to 2,600 m at San Lorenzo. YELLOW-LEGGED THRUSH Platycichla flavipes at 100 m on Isla Margarita in Venezuela (Hilty 2002), from 600 m down to 350 m in the San Salvador Valley. Ralf Strewe & Cristobal Navarro 49 Bull. B.O.C. 2004 124(1) BLACK-HOODED THRUSH Zurdus olivater 800 m in Venezuela (Hilty 2002), from 1,200 m down to 600 m in the San Salvador Valley. BROWN-CAPPED VIREO Vireo leucophrys 700 m in Venezuela (Hilty 2002), from 1,200 m down to 500 m in the San Salvador Valley. WHITE-LORED WARBLER Basileuterus conspicillatus from 750 m (Stattersfield et al. 1998) down to 450 m in the San Salvador Valley. WHITE-SIDED FLOWERPIERCER Diglossa albilatera from 1,300 m (Hilty 2002) down to 1,200 m in the San Salvador Valley. SANTA MARTA MOUNTAIN-TANAGER Anisognathus melanogenys from 1,500 m (Isler & Isler 1999) down to 1,200 m in the San Salvador Valley. ROSY THRUSH-TANAGER Rhodinocichla rosea up to 100 m in Venezuela (Hilty 2002), from 500 m down to 100 m at Tayrona (Fig. 2f). SLATY FINCH JAHaplospiza rustica occasionally to 1,000 m in Andes (Stotz ef al. 1996), from 1,200 m down to 800 m at El Recuerdo. Discussion The Sierra Nevada de Santa Marta justifiably receives wide international recognition for its importance as an unique and highly threatened enclave for native and migrant avifauna. The massif represents the world’s single-most important continental avian centre of endemism with 18 endemic species and 55 endemic subspecies, and is a highly strategic staging post for Neotropical migrant bird species travelling from the Caribbean to South America. A total of 673 bird species, including the new records presented here, have been registered in the Sierra Nevada de Santa Marta region (Strewe unpubl.). Additions are expected from records of boreal migrants and from the invasion of non-forest species as forest destruction continues. The southern slope 1s partucarly poorly studied and investigations are urgently needed there, considering that more than 90% of the natural habitats have been destroyed. Security problems, as in many other localities of the region, make access to the southern slope very difficult. The paramo region of the massif and its avifauna is practically unknown, with historical collections by Carriker (reported in Todd & Carriker 1922) and one short excursion within the rio Frio valley in April 2001 (Strewe in press, b). The paramo lies entirely within the indigenous reserves and excursions require permits from the indigenous organizations. Indications are that paramo habitats and the forest-paramo ecotone are threatened through seasonal burning and grazing. Ongoing destruction of these natural habitats is threatening especially the endemics with limited ranges, Ralf Strewe & Cristobal Navarro 50 Bull. B.O.C. 2004 124(1) low population densities and naturally localised distributions resulting from specific habitat preferences. Monitoring of the paramo habitats, their avifauna and of anthropogenic impacts on the ecosystem are of critical importance. Within the massif less than 15 % of the original forest cover remains, and despite substantive protection status on paper, the massif continues to sustain high rates of habitat loss to human colonisation and degradation. Yet little attention or effort has been taken within the last 50 years towards conducting research to aid the implementation of effective conservation measures and adequate management strategies for this highly sensitive faunal group. Data collected during fieldwork within the present project are being used to develop habitat management strategies, addressing identified threats to migrant and resident birds, and to implement conservation corridors and a network of private reserves. Other project objectives are to commercially produce bird-friendly coffee, and to establish an educational programme involving local communities in nature conservation and sustainable agronomy. As a result of the project activities, the rio Frio, San Salvador and Toribio Valleys are declared as Important Bird Areas (IBA), under a joint BirdLife International and Alexander von Humboldt Institute (Bogota) programme. Acknowledgements The studies were made possible by financial support from the National Fish & Wildlife Fund, CIM/GTZ Germany and Fundacion Pro-Sierra Nevada de Santa Marta. Many thanks to all the staff at Buena Vista and El Congo nature reserves for their assistance throughout the project. We are grateful for advice and assistance from the following: Mauricio Alvarez Rebolledo, Olga Ines Ramirez Gomes, Dorotea Cardona Hernandez, Gheynner Lobaton, Lacides Malo, Margarita M. Nieto Restrepo, Santiago Restrepo, Fernando Salazar Holguin and Sandra Sanchez. Many thanks to Chris Feare and Paul Salaman for comments on the manuscript and editorial assistance. References: BirdLife International. 2000. Threatened birds of the world. Lynx Edicions & BirdLife International. Barcelona & Cambridge, UK. Curson, J., Quinn, D. & Beadle, D. 1994. Warblers of the Americas: an identification guide. Houghton Mifflin, Boston. del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 1997. Handbook of the birds of the world, vol. 4. Lynx Edicions. Barcelona. del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 1999. Handbook of the birds of the world, vol. 5. Lynx Edicions. Barcelona. del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 2002. Handbook of the birds of the world, vol. 6. Lynx Edicions. Barcelona. Ferguson-Lees, J. & Christie, D. A. 2001. Raptors of the world. Houghton Mifflin, Boston. Fjeldsa, J. & Krabbe, N. 1990. Birds of the high Andes. Zool. Mus., Univ. of Copenhagen & Apollo Books, Svendborg. Hilty, S. L. 2002. Birds of Venezuela. Princeton Univ. Press. Hilty, S. L. & Brown, W. L. 1986. A guide to the birds of Colombia. Princeton Univ. Press. Isler, M. L. & Isler, P. R. 1999. The tanagers. Smithsonian Institution Press, Washington D.C. Renjifo, L. M., Franco-Maya, A. M., Amaya-Espinel, J. D., Kattan, G. H. & Lopez-Lanus, B. (eds.) 2002. Libro rojo de aves de Colombia. Serie Libro Rojos de Fauna, Flora y Hongos Amenazados de Ralf Strewe & Cristobal Navarro 51 Bull. B.O.C. 2004 124(1) Colombia, Instituto de Investigacion de Recursos Biologicos Alexander von Humboldt & Ministerio del Medio Ambiente, Bogota. Ridgely, R. S. & Greenfield, P. J. 2001. The birds of Ecuador, vol. 1. Cornell Univ. Press, Ithaca, New York. Rodner, C., Lentino, M. & Restall, R. 2000. Checklist of the birds of northern South America. Pica Press, Robertsbridge. Salaman, P., Donegan, T. M. & Cuervo, A. M. 2002. New distributional bird records from Serrania de San Lucas and adjacent Central Cordillera of Colombia. Bull. Brit. Orn. Cl. 122: 285-303. Sibley, D. A. 2001. The Sibley guide to birds. National Audubon Society, New York. Stattersfield, A. J., Crosby, M. J., Long, A. J. & Wege, D. C. 1997. Endemic Bird Areas of the world: priorities for biodiversity conservation. BirdLife Conservation Series No. 7. BirdLife International, Cambridge, UK. Stotz, D. F., Fitzpatrick, J. W., Parker, T. A. & Moskovits, D. K. 1996. Neotropical birds: ecology and conservation. Univ. Chicago Press. Strewe, R. (in press, a) Birds and conservation value of the San Salvador Valley, Sierra Nevada of Santa Marta, north-east Colombia. Revista Asociacion Colombiano de Ornitologia 1. Strewe, R. (in press, b) The threatened birds of the rio Frio Valley, Sierra Nevada de Santa Marta, Colombia. Cotinga 22. Todd, W. E. & Carriker, M. A. 1922. The birds of the Santa Marta region of Colombia: a study in altitudinal distribution. Ann. Carnegie Mus., vol. 14. Troncoso, P. F., van der Wolf, P. A. J. & Ahumada, J. A. 1995. The Lilac-tailed Parrotlet (Jouit batavica), a new record for Colombia. Caldasia 18(86): 147-148. Address: Ralf Strewe and Cristobal Navarro, Fundacion Pro-Sierra Nevada de Santa Marta, Calle 17 No. 3-83, Santa Marta, Colombia, e-mail (for corresponding author): ralf.strewe@t-online.de © British Ornithologists’ Club 2004 A survey of the Serrania de Jungurudo, an isolated mountain range in eastern Panama by G. R. Angehr, D. G. Christian & K. M. Aparicio Received 4 April 2003 Eastern Panama is a well-known centre of endemism for birds. In a recent analysis by BirdLife International, Stattersfield et a/. (1998) examined the distribution of restricted-range birds (those with a total world range of less than 20,000 km?) and defined 218 Endemic Bird Areas (EBAs), based on the co-occurrence in a given area of two or more of such species. Eastern Panama includes parts of two of these EBAs. The Darién Highlands EBA is defined as the highlands of eastern Panama and westernmost Colombia above 700 m. Eleven restricted-range species are entirely confined to it, with another five found both there and in other EBAs. The Darién Lowlands EBA includes the lowlands and foothills of eastern Panama and westernmost Colombia up to c.1,000 m. It has four species entirely confined to it, with another nine found both there and in other areas (Stattersfield et a/. 1998). G. R. Angehr et al. Un 2 Bull. B.O.C. 2004 124(1) Several of the species of this EBA are primarily found in foothills and so are restricted to the lower slopes of the same ranges where the highland endemics occur. In addition to the species listed by Stattersfield et a/. (1998), the restricted-range Ochraceous Wren Troglodytes ochraceus occurs in the Darién Highlands EBA, and Yellowish-green Tyrannulet Phylloscartes flavovirens and Tawny-capped Euphonia Euphonia anneae occur in the Darién Lowlands EBA. Stattersfield et al. (1998) listed Narino Tapaculo Scytalopus vicinior as a species of the Darién Highlands, but it has recently been determined (Krabbe & Schulenberg 1997) that the Darién birds belong to a newly described species, Choco Tapaculo S. chocoensis, which also has a restricted range. Three main mountain ranges run in parallel lengthwise along the isthmus in easternmost Panama (Fig. 1). The range along the Caribbean coast, the Serrania de Darién, includes the highest peak in the region, Cerro Tacarcuna (1,875 m). The Serrania de Pirre (1,550 m) occupies the centre of the isthmus, with the outlying ridge of the Altos de Quia to its south-east along the Colombian border. Along the Pacific coast, the highest part of the ranges, at the headwaters of the rios Sambu and Jaqué, is known as the Serrania de Jungurudo. The maximum elevation indicated on Zz" fae ae r —_— ? \ a = \ «A . 7 \ ey ny PANAMA Sapo Serrania del Sapo Serrania de py ee a\ NC) Sa Se (ood f Jungurud6 &. / ORGY Zoo : eu litt Wot 4 OLOMBIA Altos de Aspavé~ ge By (NF oy yh | seine Cordillera | | | 40 Mewes OCEAN de Jurad6 \ Figure 1. Mountain ranges of eastern Darién, Panama. Light grey = land above 200 m; dark grey = 500 m; black = 1,000 m. G. R. Angehr et al. 53 Bull. B.O.C. 2004 124(1) available maps (INGTG 1993) is c.1,700 m. The Serrania de Sapo extends north- west from the Jungurud6 and terminates at Cerro Sapo (1,145 m) near the town of Garachiné. To the south-east of the Jungurudo and connected to it are the ranges of the Cordillera de Jurado and the Altos de Aspave. These Pacific ranges are isolated from the Serrania de Pirre, c.30 km to the east, by the valleys of the rios Balsas and Jurado, which are below 200 m. The Caribbean and central ranges of Darién have both been well studied ornithologically. Cerro Tacarcuna was surveyed by H. E. Anthony and D. S. Ball in 1915 (Anthony 1923), by C. Handley in 1959, P. Galindo in 1963, and A. Wetmore in 1964. Cerro Pirre was visited by E. A. Goldman in 1912, by R. Benson in 1928, O. Pearson in 1938, A. Wetmore in 1961, P. Galindo in 1972, and M. Robbins in 1982 (Robbins eft al. 1985). Cana on the slopes of Cerro Pirre now has a small tourist lodge and is visited frequently by birding groups. The Altos de Quia was visited in 1970 by P. Galindo (Wetmore & Galindo 1972) and by R. Ridgely in 1975 (Ridgely & Gwynne 1989). In contrast, the Pacific ranges have been little studied. The only site that has previously been surveyed is Cerro Sapo at the northern end of the range, by T. Barbour, W. S. Brooks and C. F. Underwood in 1922 (Barbour & Brooks 1923), and D. Feathers in 1941 (Bond & Meyer de Schauensee 1944). The Serrania de Jungurudo itself has not previously been visited by ornithologists. Study Areas and Methods GRA made an initial trip to the Jungurudo area between 10-15 January 1996, ascending the southern side of the range from the upper rio Jaqué valley near the village of El] Mamey (07°28’N, 78°00’ W), and reaching 945 m on 12 January. GRA, DGC and KMA surveyed the Serrania de Jungurud6o more extensively from 8—23 August 1997, ascending from its northern side. We reached the range via the rio Sambu, camping at the last Embera Indian village on the river, Boca de Pavarando, on 8 August, and on 9 August at the junction of the rio Sambu and rio Antaral (07°43’N, 78°01°W). We then ascended the valley of the rio Antaral, camping at 195 m on 10 August, 680 m on 11 August, and 900 m on 12 August. On 13 August we established a base camp at 840 m on Cerro Antaral (07°37’°N, 78°00’W). We remained at this site until 22 August, working up to an elevation of c.1,000 m. We were unable to reach the summit of the range due to broken terrain and dense vegetation. Cloud forest on this part of the Jungurudo range begins at c.900 m. Although the best available map of the area (IGNTG 1993), originally prepared by the Raytheon Corporation from radar data obtained in 1967, indicates that the range reaches an elevation of 1,700 m, our altimeter readings suggested that its maximum elevation actually may be only about 1,200 m. In addition to walking trails and streams in the area, on 17—19 August we carried out c.130 hours of mist-netting near the base camp, using 6—8 nets, 12 m long with a 36-mm mesh. We tape-recorded vocalizations using Sony TCM-5000 portable G. R. Angehr et al. 54 Bull. B.O.C. 2004 124(1) tape-recorders with Sennheiser short shotgun microphones, and collected specimens by shotgun and by mist-netting. Results We report here observations of species of limited distribution or rare in Panama, especially restricted-range species. Endemic species of the Darién Lowlands EBA are indicated by an asterisk, and those of the Darién Highlands EBA with a double asterisk. Additional species occurring above 700 m are listed in the appendix. Selected recordings have been deposited with the Library of Natural Sounds (LNS), Cornell University, Ithaca, New York, USA, and specimens have been deposited at the Museo de Vertebrados of the Universidad de Panama, Panama City, Panama (MVUP) and at the American Museum of Natural History (AMNH), New York, USA. *CHOCO TINAMOU Crypturellus kerriae Occasional at lower elevations. One was tape-recorded at our camp at the mouth of the rio Antaral on 9 August 1997, and heard there again on 22 August. The call was also heard at our camp at 680 m on 11 August. The species is otherwise known in Panama from two specimens taken on the Altos de Quia in 1970 (Wetmore & Galindo 1972, Wetmore et al. 1984), and from sight records and calls heard above Cana on Cerro Pirre (various observers). On 21 February 1995 P. Phillips (pers. comm.) obtained the wing of one (MVUP 2206) from Embera Indian hunters in the upper valley of the rio Jaqué (07°29’N, 77°57’ W). The species is considered threatened (Vulnerable) at the global level (BirdLife International 2000). BLACK-AND-WHITE HAWK EAGLE Spizastur melanoleucus One was seen soaring high over the Jungurudo ridgetop on 20 August 1997. The species is rare in Panama and throughout its range. The only previous records from Darién have been from Cana on Cerro Pirre and from the valley of the rio Tuira (Ridgely & Gwynne 1989). PLUMBEOUS PIGEON Patagioenas plumbea Very common in both lowlands and highlands, and heard calling almost every day. Two birds were tape-recorded (LNS 96086 and 96087) and then collected by shotgun near the base camp on 14 August 1997 (AMNH 834071 and MVUP 2204 respectively). These represent the first specimens from Middle America. Both specimens had pale cream-coloured eyes and grey wing-linings, characteristic of Patagioenas plumbea (Gibbs et al. 2001). The very similar Short-billed 2 nigrirostris and Ruddy Pigeons P subvinacea also occur in Darién. However, both have red or reddish eyes. P nigrirostris has dark greyish-brown wing linings, and in R subvinacea they are cinnamon (Gibbs et al. 2001). These birds gave a distinctive three-note call (whit-mo-go), sometimes with the third note slurred (whit-mo-go ’o). The tape-recordings were compared with samples G. R. Angehr et al. 55 Bull. B.O.C. 2004 124(1) from South America obtained from the Library of Natural Sounds. They matched closely LNS 72408 from Esmeraldas, Ecuador; LNS 84089 from Pichincha, Ecuador; and LNS 80905 from Cundinamarca, Colombia. However, they differed from LNS 80834 from Cundinamarca, a distinctly four-noted call. According to Gibbs et al. (2001), calls of R plumbea are geographically variable. The closest subspecies for which Gibbs et a/. (2001) described the call, delicata of western and central Amazonia, has a three-note call. Gibbs et a/. (2001) did not provide a description of the call of chapmani of western Colombia and Ecuador. The calls of P nigrirostris and P subvinacea are both typically four-noted (Gibbs et a/. 2001). GRA also heard the call of this species near the headwaters of the rio Jaqué, on the southern flanks of the Serrania de Jungurudo, on 15 January 1996. TABLE 1 Distribution of restricted-range species of the Darién Highlands Endemic Bird Area, and of foothills species of the Darién Lowlands Endemic Bird Area, in the mountains of eastern Darién. ‘Pacific’ includes the Serrania de Jungurudo and Cerro Sapo. ‘Central’ includes the Serrania de Pirre and the Altos de Quia. ‘Caribbean’ includes Cerro Tacarcuna. Range extensions from this study are indicated with an asterisk. Note: Blue-and-gold Tanager Bangsia arcaei occurs only in the western part of the Endemic Bird Area. Species Pacific Central Caribbean Darién Highlands Tacarcuna Wood-quail Odontophorus dialeucos x Russet-crowned Quail-dove Geotrygon goldmani x x x Bare-shanked Screech-owl Otus clarkii x xX Violet-capped Hummingbird Goldmania violiceps Xx Rufous-cheeked Hummingbird Goethalsia bella x x Beautiful Treerunner Margarornis bellulus x* 5 Xx Tacarcuna Tapaculo Scytalopus panamensis x Choco Tapaculo Scytalopus chocoensis x 4 Ochraceous Wren Troglodytes ochraceus x x Varied Solitaire Myadestes coloratus x x x Sooty-faced Finch Lysurus crassirostris X Tacarcuna Bush-tanager Chlorospingus tacarcunae 4 Pirre Bush-tanager Chlorospingus inornatus xX x Yellow-collared Chlorophonia Chlorophonia flavirostris Xx Green-naped Tanager Tangara fucosa Xx Xx Pirre Warbler Basileuterus ignotus X Xx Darién Lowlands (foothills species) Choco Tinamou Crypturellus kerriae ? Xx Purplish-backed Quail-dove Geotrygon lawrencii X Stripe-cheeked Woodpecker Piculus callopterus Xx X Spiny-cheeked Antshrike Xenornis setifrons Xx Black-crowned Antpitta Pittasoma michleri Xx Xx x Tawny-capped Euphonia Euphonia anneae X Black-and-yellow Tanager Chrysothlypis chrysomelas X Xx % G. R. Angehr et al. 56 Bull. B.O.C. 2004 124(1) The species also occurs on the Serrania de Pirre, where it has apparently been overlooked until recently due to its close similarity to P nigrirostris and P subvinacea. On 2 May 1994 GRA heard several birds calling near the north end of the Pirre range above the town of El Real. On 11 April 1995 GRA, D. & L. Engleman and others observed a bird with cream-coloured eyes calling on the trail above Cana on Cerro Pirre, and several others were heard. On 30 March 2001, GRA saw and tape- recorded a bird with cream-coloured eyes giving a three-note call on the same trail. P. Coopmans (pers. comm.) heard the species commonly in the 600—1,300 m range at Cana between 30 January—9 February 1992, and tape-recorded it on 2 and 6 February (LNS 60300, 60302, 60333, 60336; catalogued as “Columba species’). Coopmans heard the species subsequently at Cana on trips in December 1994—January 1995, February 1996 and March 1998. G. Rompré (pers. comm.) saw a bird with pale eyes and heard it calling at 550 m near the north end of the Pirre range on 21 April 1995. We found Short-billed Pigeon to be rare on the Jungurud6, with one heard calling at 300 m on 11 August 1997, and greatly outnumbered by P plumbea. We did not see or hear Ruddy Pigeon. **RUSSET-CROWNED QUAIL-DOVE Geotrygon goldmani Common in the highlands near our base camp, recorded almost every day, mostly by voice. This restricted-range species is endemic to the highlands of Darién and eastern Panama province. It is otherwise known from Cerro Jefe and Cerro Brewster and the Serrania de Majé in eastern Panama province, and in Darién from Cerro Tacarcuna, Cerro Pirre, and Cerro Sapo (Wetmore 1968, Ridgely & Gwynne 1989). The species is considered Near Threatened at the global level (BirdLife International 2000). CENTRAL AMERICAN PYGMY-OWL Glaucidium griseiceps GRA heard one at the village of El Mamey on the upper rio Jaqué on 9 and 15 January 1996, and one was seen and heard at our camp in the lowlands on the rio Antaral on 9 and 10 August 1997. This rare to uncommon species is elsewhere known from Darién from the lower Chucunaque River, and from Cana and the lower slopes of Cerro Pirre (Wetmore 1968, Ridgely & Gwynne 1989). TOOTH-BILLED HUMMINGBIRD 4Androdon aequatorialis Occasional in the highlands, recorded on 13, 17 and 21 August 1997. One female was collected on 17 August (MVUP 2026). Previously recorded in Panama from Cerro Tacarcuna, Cerro Pirre and Cerro Sapo (Wetmore 1968). GREEN THORNTAIL Discosura conversii A male was seen by GRA at c.750 m on a ridge above the rio Jaqué on 13 January 1996. The species is otherwise known from Darién from near Cana on Cerro Pirre (Wetmore 1968, Ridgely & Gwynne 1989). ee G. R. Angehr et al. ow Bull. B.O.C. 2004 124(1) **RUFOUS-CHEEKED HUMMINGBIRD Goethalsia bella Very common in the highlands, recorded every day. A male and a female were collected on 17 August 1997 (MVUP 2209, 2210). One was seen also by GRA on 12 January 1996 at 900 m, above the headwaters of the rio Jaqué. This species is endemic to the highlands eastern Darién, being otherwise known from Cerro Pirre and Cerro Sapo (Wetmore 1968, Ridgely & Gwynne 1989). This species is considered Near Threatened at the global level (BirdLife International 2000). GREENISH PUFFLEG Haplophaedia aureliae Common in the highlands, recorded almost every day. One male was collected on 18 August 1997 (MVUP 2211). Known otherwise in Panama only from Cerro Tacarcuna and Cerro Pirre (Wetmore 1968, Ridgely & Gwynne 1989). *STRIPE-CHEEKED WOODPECKER Piculus callopterus Rare in the foothills, recorded on 12 August and on 22 August 1997 at 650 m. Previously recorded from Veraguas; eastern Colon Province; Cerro Azul, Cerro Jefe and Cerro Chucanti in Panama province; and in Darién from the upper Jaqué Valley and Cerro Pirre (Wetmore 1968, Ridgely & Gwynne 1989). **BEAUTIFUL TREERUNNER Margarornis bellulus Uncommon in the highlands, with individuals seen on 15, 19, and 20 August 1997. A female was collected 15 August and a male on 19 August (MVUP 1975, 1976). This Darién Highlands endemic is otherwise known from Cerro Tacarcuna and Cerro Pirre (Wetmore 1972), Altos de Quia (Ridgely & Gwynne 1989) and the Serrania de Majé (Angehr & Christian 2000). The species is considered Near Threatened at the global level (BirdLife International 2000). SHARP-TAILED STREAMCREEPER Lochmias nematura Rare in the highlands. One was seen in a steep ravine on 15 August 1997 (DGC). Otherwise known in Panama from Cerro Mali (near Cerro Tacarcuna), Cerro Pirre and the Altos de Quia (Wetmore 1972, Ridgely & Gwynne 1989). *BLACK-CROWNED ANTPITTA Pittasoma michleri This restricted-range species was rare in the highlands, recorded on 12 and 13 August 1997. It is rare but widespread in the Darién lowlands and foothills (Wetmore 1972, Ridgely & Gwynne 1989). **CHOCO TAPACULO Scytalopus chocoensis Common in wet ravines in the highlands. A pair was tending a nest with two nestlings within 40 m of our base camp, and these were collected on 19 August 1997 (tape- recorded as LNS 09089 and 09090; AMNH 834072 and 834073). Christian (2001) described the nest and nesting behaviour. In addition, two other adult males were collected, on 16 and 17 August (MVUP 2207, 2208), and a juvenile on 15 August a G. R. Angehr et al. 58 Bull. B.O.C. 2004 124(1) 1997 (LNS 09088, AMNH 834074). Two forms of Scytalopus are known from eastern Darien. Two specimens (a male and a female) collected on Cerro Pirre by O. Pearson in 1938 were originally assigned to Narifio Tapaculo S. vicinior (Wetmore 1972). In a recent revision, Krabbe & Schulenberg (1997) included the Cerro Pirre birds in a newly described taxon, S. chocoensis, whose range extends along the western flank of the Andes in Colombia and Ecuador. S. chocoensis males lack facial patterning (Krabbe & Schulenberg 1997). The Pale-throated, or Tacarcuna, Tapaculo S. panamensis is endemic to Cerro Tacarcuna. Males have a broad silvery superciliary stripe beginning above and extending behind the eye. The breeding male from the Jungurudo has a faint but definite light grey superciliary stripe and a faint greyish crescent on the cheek. The superciliary stripe is much less distinct than that of S. panamensis. The other two male specimens lack any facial patterning. Other males seen on the Jungurudo had traces of a facial pattern. Some male Scytalopus on Cerro Pirre also have a trace of a facial pattern (GRA pers. obs.). Calls of the Jungurudo birds closely resemble recordings of S. chocoensis provided by N. Krabbe. BRONZE-OLIVE PYGMY-TYRANT Pseudotriccus pelzelni Rare in the highlands. A pair was observed in cloud forest at c.1,000 m on 20 and 21 August 1997 (DGC). The species is otherwise known in Panama only from Cerro Tacarcuna and Cerro Pirre (Wetmore 1972, Ridgely & Gwynne 1989). GREEN MANAKIN Chloropipo holochlora Very common in the highlands. In Panama the species occurs from Cerro Brewster in eastern San Blas eastwards, and is rare to uncommon (Ridgely & Gwynne 1989). A nest found on 15 August 1997 was described by Christian (2001). WHITE-WINGED SWALLOW Tachycineta albiventer A group of seven was seen on the rio Sambu (DGC and KMA) during our descent of the river on 25 August 1997. This represents the second report of this species from Panama, the first being by Seutin (1998) on the rio Balsas. SOOTY-HEADED WREN Thryothorus spadix Uncommon in the highlands. Otherwise known in Panama from Cerro Tacarcuna, Cerro Pirre and the Altos de Quia (Wetmore et al. 1984, Ridgely & Gwynne 1989). ** VARIED SOLITAIRE Myadestes coloratus Very common in the highlands. Two males were collected on 17 and 18 August 1997 (MVUP 1979, 1982). This species is endemic to the eastern Darién highlands, otherwise being found on Cerro Tacarcuna and Cerro Pirre (Wetmore et al. 1984 , Ridgely & Gwynne 1989), and recently discovered on the Serrania de Majé (Angehr & Christian 2000). G. R. Angehr et al. 59 Bull. B.O.C. 2004 124(1) GREY-AND-GOLD TANAGER Tangara palmeri Uncommon in the highlands. Otherwise known in Panama from Cerro Tacarcuna, Altos de Quia, Cerro Pirre and Cerro Sapo (Wetmore ef al. 1984, Ridgely & Gwynne 1989), with recent sightings from Nusagandi in eastern San Blas province (D. Engleman, pers. comm.) and from Cerro Azul in eastern Panama province (W. Adsett & G. Seutin, pers. comm.). **GREEN-NAPED TANAGER Tangara fucosa Uncommon in the highlands. A female was collected on 21 August 1997 (MVUP 2212). The nest and nesting behaviour of a pair found on 20 August were described by Christian (2001). The species is endemic to the eastern Darién Highlands, and is otherwise known only from Cerro Mali near Cerro Tacarcuna and Cerro Pirre (Wetmore et al. 1984). The species is considered Near Threatened at the global level (BirdLife International 2000). ORANGE-BELLIED EUPHONIA Euphonia xanthogaster Common in the highlands. Otherwise known in Panama from Cerro Pirre, Altos de Quia, Cerro Sapo and the rio Jaqué valley (Wetmore et al. 1984, Ridgely & Gwynne 1989). SCARLET-BROWED TANAGER #eterospingus xanthopygius Rare, one seen at c.700 m on 11 August 1997 (DGC). Known in Panama from the Tuira River valley, Cerro Pirre, Cerro Sapo and the Jaqué River valley (Wetmore ef al. 1984, Ridgely & Gwynne 1989). **PIRRE BUSH-TANAGER Chlorospingus inornatus Very common in the highlands. Endemic to the eastern Darién highlands, and previously recorded only on Cerro Pirre and Cerro Sapo (Wetmore ef al. 1984, Ridgely & Gwynne 1989). One male was collected on 20 August 1997 (MVUP 1974). *BLACK-AND-YELLOW TANAGER Chrysothlypis chrysomelas This restricted-range species was fairly common in the highlands. It is otherwise fairly widely distributed in both western and eastern Panama, and known in Darién from Cerro Tacarcuna, Cerro Pirre, Cerro Sapo and Cerro Quia (Wetmore ef al. 1984, Ridgely & Gwynne 1989). STRIPE-HEADED BRUSH-FINCH Buarremon torquatus Two were seen by GRA at 750 m near the headwaters of the rio Jaqué on 12 January 1996. This rare to uncommon species is otherwise known from Darién from Cerros Pirre and Tacarcuna (Wetmore et al. 1984, Ridgely & Gwynne 1989). G. R. Angehr et al. 60 Bull. B.O.C. 2004 124(1) YELLOW-GREEN GROSBEAK Caryothraustes canadensis A small flock was seen at 640 m on 22 August 1997. Otherwise known in Panama only from Cerro Pirre (Wetmore ef al. 1984, Ridgely & Gwynne 1989). Conclusions The avifauna of the Serrania de Jungurudo is most similar to that of the nearby Serrania de Pirre, but also shares species with the more distant Cerro Tacarcuna. Of the 11 restricted-range species of the Darién Highlands Endemic Bird Area known to occur on Pirre, we found seven on the Jungurudo (Table 1). Four of these also occur on Cerro Tacarcuna. Except for Russet-crowned Quail-dove, Rufous-cheeked Hummingbird and Pirre Bush-tanager, previously known from Cerro Sapo, these represent the first records from the Pacific ranges of Darién. The species occurring on Pirre that we did not encounter were Bare-shanked Screech-owl Otus clarki, Ochraceous Wren 7roglodytes ochraceus, Pirre Warbler Basileuterus ignotus and Yellow-collared Chlorophonia Chlorophonia flavirostris. All of these, except the wren, usually occur at higher elevations than we were able to reach on the Jungurudo; the lower elevational limits for these species listed by Ridgely & Gwynne (1989) are 1,080, 750, 1,350 and 1,200 m respectively. Of the seven species of the Darién Lowlands Endemic Bird area that are found primarily in foothills, we found four on the Jungurudo (Table 1): two of these also occur on Cerro Tacarcuna. Of these, the records of Chocé Tinamou are the first for the Pacific ranges. Many of the new records included here represent a significant expansion in the known ranges of several species that occupy very limited geographical areas. Fortunately, there are grounds for optimism for the conservation of the restricted- range species of the Darién mountains. Most of the highlands, including the Jungurud6, have been legally protected within Darién National Park (579,000 ha), with the exception of the Pacific ranges north of Cerro Sapo. Although clearing for subsistence agriculture and logging are having a severe impact on the lowland forests of Darién, at present the highland areas are still mostly untouched. Acknowledgments The expedition of 1997 was supported in part by National Geographic Magazine, and in part by Fundacion Natura, Panama, and was carried out as part of an Important Bird Areas project for Panama, under the auspices of BirdLife International and of Fundacion Natura. Daniel Castefieda ably served as guide and organizer for the trip, and Roberto Ibafiéz, Tom Horton, Bill Hatcher and Chris MacIntosh provided companionship in the field. C. Kernan and P. Phillips organized the 1996 trp to the rio Jaqué. We thank the Embera people of Boca de Pavarando and of El] Mamey for their hospitality and their assistance. ANAM, Panama’s Natural Resources Agency, provided the permits for research and collection. We thank N. Krabbe for providing reference recordings of Scytalopus species. References: Angehr, G. R. & Christian, D. G. 2000. An omithological survey of the Serrania de Majé, an isolated mountain range in eastern Panama. Bull. Brit. Orn. Cl. 120: 173—178. Anthony, H. E. 1923. In the footsteps of Balboa. Natural History 23: 312-324. G. R. Angehr et al. 61 Bull. B.O.C. 2004 124(1) Barbour, T. & Brooks, W. S. 1923. The Sapo mountains and the Sambu Valley. A biological reconnaissance in southeastern Panama. Geographical Review 8: 221-222. BirdLife International. 2000. Threatened birds of the world. Lynx Edicions, Barcelona & BirdLife International, Cambridge, UK. Bond, J. & Meyer de Schauensee, R. 1944. The birds. Pp. 7-56 in G. Vanderbilt. Results of the fifth George Vanderbilt expedition (1941). Acad. Nat. Sci. Phil. Monogr. No. 6. Christian, D. G. 2001. Nests and nesting behavior of some little known Panamanian birds. Ornitologia Neotropical 12: 327-336. Gibbs, D., Barnes, E. & Cox, J. 2001. Pigeons and doves. A guide to the pigeons and doves of the world. Yale Univ. Press. IGNTG. 1993. Darién (Mapa Especial) 1:250,000. Instituto Geografico Nacional ‘Tommy Guardia’: Panama City. Krabbe, N. & Schulenberg, T. S. 1997. Species limits and natural history of Scytalopus tapaculos (Rhinocryptidae), with descriptions of the Ecuadorian taxa, including three new species. Pp. 47-88 in Remsen, J. V., Jr. (ed.) Studies in Neotropical ornithology honoring Ted Parker. Orn. Monog. No. 48. Ridgely, R. S. & Gwynne, J. A.1989. A guide to the birds of Panama. Second edition. Princeton Univ. Press. Robbins, M. B., Parker, T. A., & Allen, S. E. 1985. The avifauna of Cerro Pirre, Darién, eastern Panama. Pp. 198—232 in Buckley, P. A., Foster, M. S., Morton, E. S., Ridgely, R. S., & Buckley, F. G. (eds.) Neotropical ornithology. Orn. Monogr. No. 36. Seutin, G. 1998. Two bird species new for Panama and Central America: White-whiskered Hermit Phaethornis yaruqui and White-winged Swallow Tachycineta albiventer. Cotinga 9: 22-23. Stattersfield, A. J., Crosby, M. J., Long, A. J. & Wege, D. C. 1998. Endemic Bird Areas of the world: priorities for biodiversity conservation. BirdLife Conservation Series No. 7. BirdLife International, Cambridge, UK. Wetmore, A. 1968. The birds of the Republic of Panama. Part 2. Columbidae (Pigeons) to Picidae (Woodpeckers). Smithsonian Institution, Washington D.C. Wetmore, A. 1972. The birds of the Republic of Panama. Part 3. Passeriformes: Dendrocolaptidae (Woodcreepers) to Oxyruncidae (Sharpbills). Smithsonian Institution, Washington D.C. Wetmore, A., Pasquier, R. F & Olson, S. L. 1984. The birds of the Republic of Panama. Part 4. Hirundinidae (Swallows) to Fringillidae (Finches). Smithsonian Institution, Washington D.C. Wetmore, A. & Galindo, P. 1972. Additions to the birds recorded in Panama. Proc. Biol. Soc. Wash. 85: 309-312. Addresses: G. R. Angehr, Smithsonian Tropical Research Institute, Unit 0948, APO AA 34002-0948, USA, e-mail: angehrg@tivoli.si.edu; D. G. Christian, Smithsonian Tropical Research Institute, Unit 0948, APO AA 34002-0948, USA (present address: 9301 57th Avenue South, Apt. 5., Seattle, WA 98118, USA), e-mail: dgchris@I|su.edu; K. A. Aparicio, Panama Audubon Society, Apartado 2026, Balboa, Republic of Panama, e-mail: k_aparicio@yahoo.com. Appendix. Additional species observed above 700 m on the Serrania de Jungurudo. Great Tinamou Jinamus major, common; Little Tinamou Crypturellus soui, rare; Tiny Hawk Accipiter superciliosus, rare; White Hawk Leucopternis albicollis, occasional; Barred Hawk Leucopternis princeps, tare; Black Hawk-eagle Spizaetus tvrannus, occasional; Omate Hawk-eagle Spizaetus ornatus, occasional; Barred Forest-falcon Micrastur ruficollis, not uncommon; Collared Forest-falcon Micrastur Semitorquatus, rare; Crested Guan Penelope purpurascens, uncommon; Black-eared Wood-quail Odontophorus melanoleucus, occasional; Tawny-faced Quail Rhynchortyx cinctus, occasional; Ruddy Quail-dove Geotrygon montana, fairly common; Vermiculated Screech-owl Otus guatemalae, rare; Green Hermit Phaethornis guy, very common; Green-crowned Brilliant Heliodoxa jacula, common; Collared G. R. Angehr et al. 62 Bull. B.O.C. 2004 124(1) Trogon Trogon collaris, fairly common; Rufous Motmot Baryphthengus martii, rare; Red-headed Barbet Eubucco bourcierii, rare; Emerald Toucanet Aulacorhynchus prasinus, common; Yellow-eared Toucanet Selenidera spectabilis, common; Keel-billed Toucan Ramphastos sulfuratus, rare; Cinnamon Woodpecker Celeus loricatus, rare; Spotted Barbtail Premnoplex brunnescens, fairly common; Slaty-winged Foliage- gleaner Philydor fuscipennis, uncommon; Ruddy Foliage-gleaner Automolus rubiginosus, uncommon; Plain Xenops Xenops minutus, rare; Tawny-throated Leaftosser Sclerurus mexicanus, rare; Wedge-billed Woodcreeper Glyphorynchus spirurus, rare; Spotted Woodcreeper Xiphorhynchus erythropygius, very common; Western Slaty Antshrike Thamnophilus atrinucha, uncommon; Russet Antshrike Thamnistes anabatinus, uncommon; Plain Antvireo Dysithamnus mentalis, uncommon; Checker-throated Antwren Myrmotherula fulviventris, rare; Slaty Antwren Myrmotherula schisticolor, uncommon; Immaculate Antbird Myrmeciza immaculata, uncommon; Bicoloured Antbird Gymnopithys leucapsis, rare; Ocellated Antbird Phaenostictus mcleannani, rare; Spectacled Antpitta Hylopezus perspicillatus, rare; Paltry Tyrannulet Zimmerius vilissimus, rare; Olive-striped Flycatcher Mionectes olivaceus, very common; Scale-crested Pygmy-tyrant Lophotriccus pileatus, very common; White-throated Spadebill Platyrinchus mystaceus, common; Ruddy-tailed Flycatcher Terenotriccus erythrurus, uncommon; Sulphur-rumped Flycatcher Myiobius barbatus, uncommon; Tufted Flycatcher Mitrephanes phaeocercus, uncommon; Dusky-capped Flycatcher Myiarchus tuberculifer, rare; Thrush-like Schiffornis Schiffornis turdinus, common; White-ruffed Manakin Corapipo altera, very common; Grey-breasted Wood-wren Henicorhina leucophrys, very common; Tawny-faced Gnatwren Microbates cinereiventris, common; Slaty-backed Nightingale-thrush Catharus fuscater, very common; Pale-vented Thrush Jurdus obsoletus, uncommon; Slate-throated Redstart Myioborus miniatus, common; Buff-rumped Warbler Basileuterus fulvicauda, rare; Bananaquit Coereba flaveola, common; Emerald Tanager Tangara florida, common; Silver-throated Tanager TJangara icterocephala, very common; Speckled Tanager Tangara guttata, occasional; Bay- headed Tanager Zangara gyrola, fairly common; Lemon-spectacled Tanager Chlorothraupis olivacea, very common; Hepatic Tanager Piranga rubra, rare; Dusky-faced Tanager Mitrospingus cassinii, occasional; Slate-coloured Grosbeak Saltator grossus, fairly common; Chestnut-capped Brush-finch Buarremon brunneinucha, common; Scarlet-rumped Cacique Cacicus uropygialis, common. © British Ornithologists’ Club 2004 The downy young of grey teal (Anatidae) with first descriptions of the ducklings of Madagascar Teal Anas bernieri and Indonesian Teal A. gibberifrons by H. Glyn Young & Mark Brayshaw Received 17 April 2003 The grey teal are a group of small (c.300—700g) Anas dabbling ducks from Madagascar, Asia and Australasia. Grey teal are predominantly tree cavity nesters and, in many places, restricted to mangrove forest and associated wetlands. Modern species in this group are often highly dispersive and it is probable that their ancestors spread along coasts and visited islands throughout the Indian Ocean during the H. Glyn Young & Mark Brayshaw 63 Bull. B.O.C. 2004 124(1) Pleistocene, when sea levels were much lower than today (Young 2002). Teal may have island-hopped westwards to Madagascar when land, now submerged, held mangrove and, possibly, populations of grey teal. The number of grey teal taxa recognised as full species has, in recent years, ranged from two (Ripley 1942) to five (Livezey 1997, Kear in press). The grey teal were often further grouped with three species of brown teal from New Zealand (see e.g. Delacour & Mayr 1945) to form the austral teal; however, the close link with these species is no longer considered valid (Young et al. 1997, Daugherty et al. 1999, Kennedy & Spencer 2000). In this paper we follow Livezey (1997) and recognise five species: Madagascar or Bernier’s Teal Anas bernieri from western Madagascar, Andaman Teal A. a/bogularis from the Andaman Islands (India), Indonesian or Sunda Teal A. gibberifrons from Sumatra to Sulawesi (Indonesia), Grey Teal A. gracilis from eastern Indonesia, Australia, New Caledonia and New Zealand (including the recently extinct A. gracilis remissa of Rennell Island; see Ripley 1942, Young et al. 1996) and Chestnut Teal A. castanea from Australia. The recently extinct (c.1710; BirdLife International 2000) Sauzier’s Teal A. theodori of the Mascarene Islands may also have been a grey teal (Mourer-Chauviré et al. 1999). Grey and Chestnut Teal are common and well studied (see e.g. Marchant & Higgins 1990). The remaining species, however, are much less well known and many areas of their biology are as yet undescribed. The range of the Indonesian Teal and extent of any overlap with that of the Grey Teal are uncertain. The development of a captive population of the Endangered Madagascar Teal at Jersey Zoo (Durrell Wildlife Conservation Trust) has allowed a close study of this species that is not practical in the wild: the nest and eggs were first described in 2001 (Young et al. 2001). Andaman and Indonesian Teal have also been poorly studied in the wild and have often been overlooked by ornithologists who accepted the view that, although dissimilar, they were conspecific with Grey Teal (Young 1996) as A. gibberifrons. The downy young of Madagascar Teal have never been described, and those of Indonesian Teal not adequately. Livezey (1991), in his study of dabbling duck morphology, included data on the downy young of Grey (as A. gibberifrons), Chestnut and Andaman Teal; however, he did not include Indonesian Teal as a separate species and no material of A. bernieri was available to him. At Jersey Zoo, 130 Madagascar Teal (1998—2002) and 11 Indonesian Teal (1998— 2001) have been hatched from nine and an unknown number of wild founders respectively. Several downy young of both species were drawn and photographed at three to five days old when the plumage was bright (Class IA; Gollop & Marshall 1954). These two species are described below and depicted in Fig. 1 with descriptions of Grey, Chestnut and Andaman Teal based on published material (see references below) and one museum specimen of Andaman Teal. Nomenclature follows Livezey (1991) and Nelson (1993). H. Glyn Young & Mark Brayshaw 64 Bull. B.O.C. 2004 124(1) Species accounts GREY TEAL 4nas gracilis Sources Downy young were described by Delacour (1956; includes colour plate), Cunningham & Welch (1955; includes black and white plate), Frith (1982; includes black and white plate) and Marchant & Higgins (1990; includes colour plate). Description by Phillips (1923) presumably referred to A. gibberifrons (see below). Plumage Dull grey-brown above and off-white below. Crown, nape, back, wings and sides to just below wings, dark brown. Underparts, mostly dull white, washed cream. At junction of foreneck and breast, the down is duller. Thighs, dark brown. Face light buff with pinkish tinge at the rear. Chin white but face showing warmer brown tones. Faint dark brown eyestripe extends from bill, through eye to ear-coverts. Narrow light-brown supra-orbital stripe, becomes light brown distally. Throat and foreneck, dull white. From back to tail, the down is hair-like and pale dark brown. Two pale whitish spots on back; shoulder spot is smaller than rump spot. Tail is dark brown; open pennaceous and hair-like. Posterior margin of upperwing (‘primaries’ and ‘secondaries’ (Nelson 1993) 1.e. the wing areas where these wing feathers will later emerge) is white, the rest, dark brown. Radius—ulna region of underwing is dark brown; the posterior margin is a narrow white band, the remainder, white, tipped brown. Bare parts Bill is dark slaty black or blue-grey, brown tipped and horn-coloured in the middle, the underside is pinkish. Legs are slate-grey, the webs brownish. Tris Dark grey-brown. CHESTNUT TEAL Anas castanea Sources Downy young were described by Phillips (1923), Delacour (1956; includes colour plate), Frith (1982; includes black and white plate) and Marchant & Higgins (1990; includes colour plate). Plumage Similar to Grey Teal, but darker; whitish areas are replaced by yellow and grey plumage is heavily suffused with chestnut. Grey-brown above, underparts paler with pale yellow wash; there are two conspicuous brown stripes on head. Crown, hindneck and eyestripe are dark brown with a dark cheek stripe extending to ear- coverts. Rest of sides of head, including supra-orbital stripe are light rufous-brown. Foreneck dull white. Shoulder and rump spots are both small and pale. Tail is dark brown. Upperwing is dark brown; the trailing edge (‘primaries’ and ‘secondaries’ see above) are dull white. The underwing is dull brown. Undertail-coverts and vent are dark brown. Bare parts No published details; however, considered similar to Grey Teal (Fullagar pers. comm.). Bull. B.O.C. 2004 124(1) 65 H. Glyn Young & Mark Brayshaw ‘MeYyskelg Ie] “SUuosfidaqgis “py [eI], URISOUOPUT (JYSLI IOMO]) S14aIU4aq ‘p [BIL IeOseSepey] (IJ IOMO]) ‘s1“pjnsoq]p ‘py [kay uewepuy (eU99) ‘paunjspo ‘py [eal ynuysoyD (Ys doy) ‘s7p19p48 spup ea, AoIH (4J9] doy) :[eo} Asis Jo SunoA Aumop oy] “| ons14 TOO les ry oj ~~ oe) ’ I H. Glyn Young & Mark Brayshaw 66 Bull. B.O.C. 2004 124(1) Tris No published details; however, considered similar to Grey Teal (Fullagar pers. comm.). ANDAMAN TEAL Anas albogularis Sources Brief descriptions were given by Phillips (1923) and Delacour (1956; includes colour plate). Unpublished black-and-white drawings of one museum specimen (BMNH 1927.2.1.2) were made by Julian Hume and used in preparation of Fig. 1. Plumage Similar to Grey Teal, grey-brown above with duller underparts. Facial patterns may vary (as they do in adults, see Grimmett et al. 1998). Eyestripe and cheek-stripe may be dark with a buffy supra-orbital stripe and cheeks. However, eyestripe and supra-orbital stripes may be lacking altogether, and, occasionally, face may be entirely dark brown with one small line or two elongated white spots above the eye and another one below. Shoulder and rump spots are small and pale, trailing edge to upperwing (‘primaries’ and ‘secondaries’ see above) is whitish. Bare parts No published details. Peter Scott (Delacour 1956, Plate XI) painted the bill dark grey or slaty-black. Tris No published details. Peter Scott (Delacour 1956, Plate XI) painted the iris dark. INDONESIAN TEAL Anas gibberifrons Sources No published details. However, brief description of Grey Teal A. gibberifrons by Phillips (1923) was of a specimen collected in the Celebes (now Sulawesi, Indonesia) and thus presumably Indonesian Teal. Living ducklings at Jersey Zoo (1998-2001). Plumage Brown upperparts, white below. Cap almost black, the eyestripe is dark and narrow, not joining the nape. Cheek-stripe is narrow, darker and broader towards ear and does not join nape. The supra-orbital and suborbital stripes are broad and brown. The cheeks, chin and breast to legs are brown, the vent and large shoulder and rump spots are pale. Upperparts and wings are dark grey, the trailing edge of the upperwing are off-white. Bare parts Bill, legs and webs dark grey. Tris Dark grey-brown. MADAGASCAR TEAL Anas bernieri Source Living ducklings at Jersey Zoo (1998-2002). Plumage Grey above and off-white below, almost like a grey-and-white young of shelduck Zadorna sp. Grey cap and nape. Face appears pale: eyestripe is narrow and does not reach the nape. The cheek-stripe is reduced and appears as a small ear spot H. Glyn Young & Mark Brayshaw 67 Bull. B.O.C. 2004 124(1) with a little of the stripe remaining below the eye at the base of the bill. The supra- orbital stripe is large and yellowish white, contrasting a little with the cheek and suborbital stripe. Back is grey with white shoulder and rump spots joining to form a white band from the vent area to the scapular region leaving a large ‘island’ of grey from the thigh to the flanks. Trailing edge of the wing is white, forming a pale band that may take up half of the wing and joins at the shoulder with the shoulder-rump band. Bare parts Bill is pinkish grey with pink edges and pink underside. Bill of some individuals may be entirely pink. Legs pinkish grey, webbing pink with greyer centres Tris Dark, centre brown. Discussion The morphology of grey teal ducklings further emphasises the distinct nature of Madagascar Teal within this otherwise homogenous group of dabbling ducks. The young of Grey and Chestnut are differently coloured, as are the adults, even though these species are considered to be similar in reproductive behaviour (Prawiradilaga 1985) and in their genetic makeup (Sraml et a/. 1996, Young et al. 1997). The variable plumage of adult Andaman Teal is mirrored in the patterning of its downy young. The young of Grey and Indonesian Teal are quite distinct from one another; the brown faces of young Indonesian Teal contrast with the grey coloration of the Grey Teal. Whilst the difference between these ducklings may be of little additional taxonomic importance, it is a further tool in the identification of breeding birds in eastern Indonesia and the subsequent mapping of the ranges of the two species. Madagascar Teal (Endangered; BirdLife International 2000) and Andaman Teal (Endangered; TWSG 2001) are already threatened with extinction. The loss of suitable habitat throughout Indonesia will only increase the chances of Indonesian Teal also becoming extinct, a risk that is not reduced by the dearth of information on their distribution and habitat requirements. Acknowledgements We thank The Durrell Wildlife Conservation Trust for allowing us access to the captive populations of Madagascar and Indonesian Teal. Janet Kear was encouraging and supportive throughout all parts of the research into Anas bernieri and made valuable comments on this study of ducklings. Julian Hume and Peter Fullagar read the manuscript and provided personal observations and drawings of A. albogularis and photographs of A. gracilis and A. castanea respectively. Murray Williams kindly read through the paper and made helpful suggestions. References: BirdLife International. 2000. Threatened birds of the world. Lynx Edicions, Barcelona & BirdLife International, Cambridge, UK. Cunningham, J. M. & Welch, E. O. 1955. The Grey Teal in New Zealand: some nesting and plumage notes. Emu 55: 303-309. Daugherty, C. H., Williams, M. & Hay, J. M. 1999. Genetic differentiation, taxonomy and conservation of Australasian teals Anas spp. Bird Conservation International 9: 29-42. H. Glyn Young & Mark Brayshaw 68 Bull. B.O.C. 2004 124(1) Delacour, J. 1956. The waterfowl of the world, vol. 2. Country Life, London. Delacour, J. & Mayr, E. 1945. The family Anatidae. Wilson Bull. 57: 4-54. Frith, H. J. 1982. Waterfowl in Australia. Angus & Robertson, London. Gollop, J. B. & Marshall, W. H. 1954. A guide for ageing duck broods in the field. Mississippi Flyway Council Technical Section. Grimmett, R., Inskipp, C. & Inskipp, T. 1998. Birds of the Indian Subcontinent. Christopher Helm, London. Kear, J. (ed.) In press. Ducks, geese and swans. Oxford Univ. Press. Kennedy, M. & Spencer, H. G. 2000. Phylogeny, biogeography, and taxonomy ofAustralasian teals. Auk 117: 154-163. Livezey, B. C. 1991. A phylogenetic analysis and classification of recent dabbling ducks (tribe Anatini) based on comparative morphology. Awk 108: 471-507. Livezey, B. C. 1997. A phylogenetic classification of waterfowl (Aves:Anseriformes), including selected fossil species. Ann. Carnegie Mus. 66: 457-496. Marchant, S. & Higgins, P. J. 1990. Handbook of Australian, New Zealand and Antarctic birds, vol. 1. Oxford Univ. Press. Mourer-Chauviré, C., Bour, R., Ribes, S. & Moutou, F. 1999. The avifauna of Réunion Island (Mascarene Islands) at the time of the arrival of the first Europeans. Pp.1—38 in Olson, S. L. (ed.) Avian paleontology at the close of the 20th century. Proceedings of the 4th International Meeting of the Society of Avian Paleontology and Evolution, Washington, D.C., 4-7 June 1996. Smithsonian Contribution to Paleobiology 89. Smithsonian Institute, Washington, D.C. Nelson, C. H. 1993. The downy waterfowl of North America. Delta Station Press, Deerfield. Phillips, J. C. 1923. A natural history of the ducks, vol. 2. Houghton Mifflin, Boston. Prawiradilaga, D. M. 1985. A comparative study of the courtship behaviour of the Grey Teal (Anas gibberifrons) and Chestnut Teal (Anas castanea). M.Sc. thesis. Univ. of New England, Armidale, Australia. Ripley, S. D. 1942. A review of the species Anas castanea. Auk 59: 90-99. Sraml, M., Christidis, L., Easteal, S., Horn, P. & Collet, C. 1996. Molecular relationships within Australasian waterfowl (Anseriformes). Australian J. Zool. 44: 47-S8. TWSG 2001. Threatened waterfowl species and subspecies. [UCN Threatened Waterfowl Specialist Group News 13: 2-4. Young, H. G. 1996. Grey teals in Asia. Bull. Oriental Bird Cl. 43: 54-57. Young, H. G. 2002. Predicting the ecology of Madagascar’s endemic dabbling ducks using captive populations and related taxa: implications for conservation. Ph.D. thesis. Univ. of Kent, Canterbury, UK. Young, H. G., Lewis, R. E. & Razafindrajao, F. 2001. A description of the nest and eggs of the Madagascar Teal Anas bernieri. Bull. Brit. Orn. Cl. 121: 64-67. Young, H. G., Sorenson, M. D. & Johnson, K. P. 1997. A description of the Madagascar Teal Anas bernieri and an examination of its relationships with the Grey Teal A. gracilis. Wildfowl 48: 174— 180. Young, H. G., Tonge, S. J. & Hume, J. P. 1996. Review of Holocene wildfowl extinctions. Wildfowl 47: 166-180. Address: H. Glyn Young and Mark Brayshaw, Durrell Wildlife Conservation Trust, Les Augrés Manor, Trinity, Jersey JE3 SBP, UK, e-mails: Glyn. Young@durrell.org and Mark.Brayshaw@durrell.org © British Ornithologists’ Club 2004 Lance Woolaver et al. 69 Bull. B.O.C. 2004 124(1) Sighting of Van Dam/’s Vanga Xenopirostris damii (Schlegel, 1866) in mangroves in north-west Madagascar by Lance Woolaver, Rina Nichols, Felix Razafindrajao & Frank Hawkins Received 27 April 2003 Van Dam’s Vanga Xenopirostris damii (Schlegel, 1866) is known from only three locations in Madagascar, where it is endemic (Fig. 1). It is currently classified as Endangered (BirdLife International 2000). The type specimens were collected in 1864 from the Ambazoana River valley (Schlegel 1866), not as usually reported on the Ampasindava Peninsula, but c.50 km further north near Ambaro Bay (Dee 1986). This species has not been recorded in this area since, although there has been little survey effort. Subsequent sightings have been from western Madagascar, where the bird was discovered in 1928 in the old-growth dry deciduous forest of Ankarafantsika, c.450 km to the south-west of the type locality (Lavauden 1932). This site includes the Ampijoroa Forest Station where the species is regularly seen. Van Dam’s Vanga has also been recorded in the dry deciduous forest of Analamera in the far north of Madagascar (Hawkins et al. 1990). This note describes the sighting of a single male in a mangrove forest south of the village of Ankazomborona, near the Ampasindava peninsula, c.30 km north-east of the type locality at Ambazoana. Surveys were carried out in the mangrove Avicennia marina forest to the south of the village of Ankazomborona. They took place over five days (116 person hours), between 11 and 24 March 2001, and between 0800 h and 1330 h. Approximately 6 km/? (2 x 3 km) was surveyed each day, on foot, such that 30 km? (10 x 3 km) in total was covered by a team of four people. The bird was seen on 21 March at 1010 h (13°23’S, 48°47’E), c.1.5 km inland from the coast and 30 km north-east of the locality (13°35’S, 48°40’E) where the type specimens were collected in 1864 (Dee 1986). The vanga was perched on a branch, 2 m above the ground in a mangrove tree. It was gaping slightly and was silent. It was observed for three minutes with binoculars (8 x 42 magnification) from a distance of < 5 m. The thickness and darkness of the bill were the most immediately striking features. Both the upper and lower mandibles were uniformly dark grey, almost black. The slight terminal hook of the upper mandible was clearly visible. The forehead, crown and ear-coverts were very dark, appearing uniformly black. The mantle, scapulars, back, rump, tail, wing-coverts and flight feathers appeared similarly uniformly black, rather than charcoal-grey as described by Morris & Hawkins (1998), but this could have been because of the strong ambient light. The bright white chin, collar and Lance Woolaver et al. 70 Bull. B.O.C. 2004 124(1) belly contrasted with the dark upper plumage. The legs and feet were dark grey. The iris appeared very dark but the exact colour was not determined. The combination of dark bill and whitish chin and throat eliminates other Xenopirostris vangas, whilst the thick bill eliminates Western Tylas Vanga Zylas eduardi albigularis. Chabert’s Vanga Leptopterus chabert is considerably smaller with a short bill and conspicuous blue eye-ring, except in the juvenile which has conspicuous white markings on the wings. There are no other confusion species. The vanga was seen in mangrove forest consisting entirely of Avicennia marina trees 4—6 m tall. The tree in which the bird was perched was on the edge of a small (c.0.5 ha) open lake that was 20-60 cm deep. Similar-sized lakes were scattered throughout the forest. Healthy regeneration of young trees provided a dense undergrowth and complete canopy cover, apart from over the small lakes. The substrate within the forest consisted of mud covered by 2 to 5 cm of water and was interspersed with a system of small shallow ponds (2—5 m in diameter) joined by small channels. The ponds were rarely deeper than 30-40 cm. The mangrove forest itself was only 2 m above high water. The forest was relatively undisturbed. This sighting is significant as it represents the only record of Van Dam’s Vanga in this area of Madagascar since the type specimens were collected in 1864. It is also the first record of this species in mangrove forest. Previous records suggested that Van Dam’s Vanga is restricted to primary dry deciduous forest (Hawkins et al. 1990, Langrand 1990, Morris & Hawkins 1998). Undisturbed mangrove forest along the north-western coast of Madagascar should not be overlooked as potential habitat for Van Dam’s Vanga. Our finding of only one individual during our survey suggests that the species is rare in mangroves, similar to Western Tylas Vanga (Hawkins 1995). Nevertheless, if Van Dam’s Vanga is utilizing significant areas of the extensive mangrove forest along the north-western coast of Madagascar, its global abundance may be greater than previously thought. Further surveys are clearly needed to confirm its conservation status. Acknowledgements We are grateful to Mr Ndramora and Mrs Begora Frang¢oise for their hospitality during our stay in Ankazomborona. Without the expert guidance of Mr Adazandry Sola dit Zaman’i Ampemba, we would still be lost in the mangroves. We would like to thank Mr & Mrs Laurie Boswell of Nosy Be for their kind help. Richard Lewis and Joanna Durbin provided excellent support from the Durrell Wildlife Conservation Trust office in Antananarivo. Roger Safford’s valuable comments greatly improved a previous draft. References: BirdLife International. 2000. Threatened birds of the world. Lynx Edicions, Barcelona & BirdLife International, Cambridge, UK. Dee, T. J. 1986. The endemic birds of Madagascar. International Council for Bird Preservation, Cambridge, UK. Langrand, O. 1990. Guide to the birds of Madagascar. Yale Univ. Press, New Haven. Lavauden, L. 1932. Etude d’un petite collection d’oiseaux de Madagascar. Bull. Mus. Hist. Paris. 4: 629-640. Lance Woolaver et al. 71 Bull. B.O.C. 2004 124(1) Hawkins, A. F. A., Chapman, P., Ganzhorn, J. U., Bloxam, Q., Tonge, S. & Barlow, S. 1990. Vertebrate conservation in Ankarana Special Reserve, Northern Madagascar. Biological Conservation 54: 83— 110. Hawkins, A. F. A. 1995. Recent observations of the Western Tylas Vanga, Zylas (eduardi) albigularis. Bull. Afr. Bird Cl. 2: 13-16. Morris, P. & Hawkins, F. 1998. Birds of Madagascar. A photographic guide. Pica Press, Robertsbridge. Schlegel, H. 1866. List of the most remarkable species of mammals and birds collected by Messrs Fr. Pollen and D. C. van Dam in Madagascar. Proc. Zool. Soc. Lond. 1866: 419-426. Addresses: Lance Woolaver (corresponding author) and Rina Nichols, Wildlife Preservation Trust Canada, 120 King St., Guelph, Ontario, NIE 4P8, Canada, e-mail: lancewoolaver@hotmail.com. Felix Razafindrajao, Durrell Wildlife Conservation Trust, BP 8511, Antananarivo 101, Madagascar. Frank Hawkins, Conservation International, BP 5178, Antananarivo 101, Madagascar. © British Ornithologists’ Club 2004 A previously unidentified museum specimen of Plain-tailed Nighthawk Nyctiprogne vielliardi (Caprimulgidae) by Nigel Cleere Received 29 Fuly 2003 The Plain-tailed Nighthawk Nyctiprogne vielliardi is endemic to the rio Sao Francisco Valley in north-eastern Brazil and is probably the least known of all Neotropical nightjars (Cleere 1998, 1999, Holyoak 2001). It is also the most recent caprimulgid discovery from South America, two specimens, an adult male holotype and a juvenile male paratype, having been collected near Manga, Bahia in October 1987 and described within the genus Chordeiles seven years later (Lencioni-Neto 1994). The species was next found near Januaria, near Mocambinho and near Pirapora in northern Minas Gerais and studied in the field, although no new specimens were collected (Whitney ef a/. 2003). These studies also led to its generic reassignment from Chordeiles to Nyctiprogne, comments on the whereabouts of the two types and documented the existence of a third, hitherto unidentified museum specimen that was collected near Mocambinho, Minas Gerais in April 1994. The holotype was confirmed as being deposited in the Museu de Zoologia da Universidade de Sao Paulo (MZUSP), the paratype was reported as not being held in a public institution and the Mocambinho specimen was recorded from the Laboratory of Ornithology, Universidade Federal do Rio de Janeiro (UFRJ). No further localities or specimens are currently known for this taxon. During an extensive examination of the Caprimulgidae material held in the American Museum of Natural History, New York (AMNH), I located a specimen from the rio Sao Francisco that matched the description of Nyctiprogne vielliardi. Nigel Cleere 72 Bull. B.O.C. 2004 124(1) The bird, an adult male (AMNH 241910) and labelled only as Nyctiprogne, was collected at Barra, Bahia, 430 m, by E. Kaempfer (field no. 5028) on 21 April 1926. I noted that it was extremely similar to Nyctiprogne leucopyga but lacked the white median tail-band of that species, although it had faint, vestigial white markings, below the uppertail-coverts on the inner webs of the four inner tail feathers (R1— R4). It also had a small buffish spot on either side of the lower throat. The biometrics were flattened wing 129 mm, tail length 86 mm and bill to skull 9.4 mm. This newly identified specimen of Nyctiprogne vielliardi represents only the fourth known for this species and is the only one held outside of Brazil. It is also the oldest of the four and comes from a new locality along the rio Sao Francisco. Barra is situated at the mouth of the rio Grande (Paynter & Traylor 1991) and is approximately 160 km south of the type locality at Manga and 675 km north of Pirapora, which currently represent the northern and southernmost limits of this species’ range. Acknowledgements I would like to thank Joel Cracraft for granting me access to the collections held in the American Museum of Natural History, and Paul Sweet and Peter Capainolo for all their help whilst working there. I am also extremely grateful to Robert Prys-Jones and Paul Salaman of The Natural History Museum/Project Biomap for giving me the opportunity to return to New York. References Cleere, N. 1998. Nightjars. A guide to nightjars and related nightbirds. Pica Press, Robertsbridge. Cleere, N. 1999. Family Caprimulgidae (Nightjars). Pp. 302—386 in del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) Handbook of the birds of the world, vol. 5. Lynx Edicions, Barcelona. Holyoak, D. T. 2001. Nightjars and their allies. The Caprimulgiformes. Oxford Univ. Press. Lencioni-Neto, F. 1994. Une nouvelle espéce de Chordeiles (Aves: Caprimulgidae) de Bahia (Brésil). Alauda 62: 242-245. Whitney, B. M., Pacheco, J. F.,, Fonseca, P. S. M. da, Webster, R. E., Kirwan, G. M. & Mazar Barnett, J. 2003. Reassignment of Chordeiles vielliardi Lencioni-Neto, 1994, to Nyctiprogne Bonaparte, 1857, with comments on the latter genus and some presumably related chordeilines (Caprimulgidae). Bull. Brit. Orn. Cl. 123: 103-112. Paynter, R. A. & Traylor, M. A. 1991. Ornithological gazetteer of Brazil. 2 vols. Mus. Comp. Zool., Cambridge, Mass. Address: The Bird Group, Dept. of Zoology, The Natural History Museum, Akeman Street, Tring, Herts. HP23 6AP, UK, e-mail: cleere@churr.freeserve.co.uk © British Ornithologists’ Club 2004 INSTRUCTIONS FOR AUTHORS Authors are invited to submit papers on topics relating to the broad themes of taxonomy and distribution of birds. Descriptions of new species of birds are especially welcome and will be given priority to ensure rapid publication, and may be accompanied by colour photographs or paintings. 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Papers should follow the general style: Title — lower case, centred, bold by Author(s) — lower case, centred, italics Introductory section without a heading Primary headings — lower case, centred, bold Secondary headings — left justified, lower case, italics, bold English names of animals should begin with capitals; give English name at first mention of every species. Numerals — thousands separated by commas, e.g. 1,000, 12,000 Units of measurement, SI. Space between values and unit, e.g. 12.1 g Statistical tests in the form: (r,, = 3.12, P< 0.01). (C°,=7.31, ns.) Citations to references in text: Author (Date); Author & Author (Date): if three or more authors — Author ef al. (Date); or (Author(s) Date) etc. References: Author, A. (or Author, A. & Author, B.) Date. Title of paper. Title of journal in italics. Volume: pages. Author, A. Date. Title of book in italics. Publisher, place of publication. Author, A. Date. Title of paper/chapter. Jn Editor, A & Editor, B. (Eds.) 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After publication, authors will be sent, free of charge, a PDF file of their paper, which that can be used to prepare reprints. Bulletin of the British Ornithologists’ Club ISSN 0007-1595 Edited by Professor Chris Feare & Guy M. Kirwan Volume 124, Number 1, pages 1-72 CONTENTS Chath ANMOUNCOMRERG .. 5...0i0snccn0sensivacnvcnseoinctinisnenanncndestivaepsupsiawise apenas sn oasiaicnbesieeneseaenee aetna 1 DICKERMAN, R. W. Notes on the type of Bubo virginianus SCIAriVENtHIS ..........+:0+1seceerereeeerere 5 FREILE, J. F. & CHAVES, J. A. Interesting distributional records and notes on the biology of bird species from a cloud forest reserve in north-west Ecuador ............2.00sc:ccerssessessnssr0s 6 KUMAR R., S. & SINGH, P. A new subspecies of Sclater’s Monal Lophophorus sclateri from western Arunelial Pradesh, [dia q. ....20< nF Om GP Scke Cee Sis a9 (7) oam tenon cnenen nvaee 00 We | mine mmaes' am ot a S8d- Bed 89d Sd Spd Std Sed “SSid> | =D) Tarsus distal w Se wm Tarsus proximal w Tarsus | 9 Tail | Wing | Ct Ear-tuft | AuricularBristle | 8 rC Rictal bristle | be Maxilla d at cere (¢) L0 COI (€1) $0 8 el Culmen | from cere (u) ds sisuanquiad (u) ds (saoei [e}UaUTIUOD) snjoydasopids (u) as Ipau{jp (U) as 114 SNYIUAYAOLAJII (Uu) ds apaual (u) ds suaasafna (ANH) fuumuuffoyoptys oAN] luupufjoyo)iy) Jo ada], ‘(QO0Z) 7? Ja UaSsnUseY WO, s7suanquad ‘C uo Kyep {(eyep ‘}qndun) YOd Pur (6661) 7? J2 OPOpIAy WO. 1padfjp ‘CE Uo ved ‘(dysuim wos sourysip) [fepsoys = s ‘(premut Areuttid 193no wo. posoquinu) Arewiud = g ‘yypim = m ‘uydap = p ‘yy3ua] = J “AjoAoodsa. sapts 1Y3tI Udt) Io] JO Orv SOY} \Poyudsoid ov SJUSLUO.ANSROLU OM} DOYA\ SadA] OY] JO 9SOY) MO[Oq popnyour ore MMHG Aq piig oat] JO Udye} syUoUIDINSeKaPy “soloods se]IUWISs pue ruupUffoyos1y) ‘EC JO UouUIdads 9dAq Jo (UU UT) S}UOLUDINSBOLU US bate vil D. H. Warakagoda & PC. Rasmussen 92 Bull. B.O.C. 2004 124(2) The bill of thilohoffmanni is markedly narrower, less arched, and appears longer and straighter near the tip than that of rufescens. The rictal bristles of thilohoffmanni are slightly to much longer than those of rufescens. The facial disk of thilohoff- manni lacks any hint of a dark rim and the feathers are uniform in colour throughout their length (vs. a moderately prominent dark rim to the facial disk, with the facial disk feathers palest immediately proximal to the dark rim in rwfescens), thus thilohoffmanni has a much plainer, more uniform facial pattern than rufescens. The feathers of the facial disk rim of thilohofjmanni are softer and less stiffened, and diffuse-tipped with slightly lengthened shafts or auricular extensions (vs. stiffened, with straight, compact tips in rufescens). The pale supercilium and front of the forehead of thilohoffmanni are weaker, more rufescent, and more barred than in rufescens (which has very prominent whitish supercilia), and show less contrast with the crown colour and pattern. In thilohoffmanni, the feathers that would in other scops-owls be elongated as ear-tufts are essentially undifferentiated, being marked as for adjacent feathers (but perhaps slightly more heavily barred than surrounding feathers), soft and unstiffened, with rounded tips like the adjacent feathers (vs. rather long and pointed, stiff ear-tufts with specialised markings in rufescens). The feathers of the upperparts of thilohoffmanni entirely lack whitish subtermi- nal triangles (vs. prominent and generally distributed whitish subterminal triangles from the crown to the rump in rufescens). The general colour of the upperparts is distinctly more uniform and more rufous above in thilohoffmanni than in rufescens (in which most specimens are dark warm brown above, although a few have more rufous-brown upperparts, and thus are intermediate in colour between typical rufescens and thilohoffmanni). The scapular spots present in almost all species of scops-owls (at least as adults) are obsolete in thilohoffmanni, in which the scapulars are only slightly paler rufous than the surrounding feathers, and are similarly marked to the surrounding feathers (vs. rufous-buff but fairly distinct and heavily marked scapular spots in rufescens). The wings of thilohoffmanni have a great deal of black proximally and on the inner webs (vs. rufous-brown in rufescens), and the wing banding of thilohoffmanni is comprised of even-width, rather weak rufous-buff bands alternating with narrowly dark-outlined rufous bands (vs. moderately to boldly, broad-banded dark brown and narrower buff wing-bands in rufescens). The undersurface of the outer primaries of thilohoffmanni is blackish except for the outer webs and tips, whilst the bases of the inner primaries are more boldly banded (vs. the entire undersurface of the remiges being rather boldly banded with broad dark and narrow pale bands in rufescens). The primary-coverts and alula are blackish except at their very tips, and are markedly and contrastingly different from the surrounding feathers in thilohoff- manni (vs. coloration and banding similar to the surrounding feathers in rufescens). The throat of thilohoffmanni is weakly marked, mostly with fine dark barring and only extremely fine dark streaking (vs. distinctly dark-streaked in rufescens). The ground colour of the underparts of thilohofjmanni is a somewhat colder, less D. H. Warakagoda & PC. Rasmussen 93 Bull. B.O.C. 2004 124(2) +3 +3 ae ¥ +2 © +2 Q .N \ = \O 7 alfredi \~ ; ° | 9 Pall Cc \ / +1 wo +1 o / ; wh The a a as 9 ~N Pz spilocephalus / © Z P wu 0 U 0 / os a oe a oe w) Z / thilohoffmanni “er 7 /rufescens -] 1 o- Se Pel wp ; ou -2 oe ireneae ~ a) — _ ear-tuft! a : =a a =] +1 +2 +3 i -3 2 =| 0 rs +2 +3 0 facial bristles, é P Pe +<— ear-tuft| PC-1 wing/tarsus | Sears <—— bristle |, wing! Pp(C-j billsize, ear-tuft!|——> a b Fig. 2a—c. Graph of loadings for individual specimens from principal components analyses (PCAs) for (a) skin measurements for Otus thilohoffmanni and O. rufescens only; (b) skin measurements for O. thilohoffmanni and other spilocephalus related species; and (c) skeletal measurements for a O. thilohoffmanni and two related species. - om “ na s S ‘i ~ 8 OE ds thilohoffmanni yellowish rufous than that of almost all specimens examined of rufescens (one specimen of rufescens had darker and browner underparts than the others, but these were still more ochraceous than PC-1 general size-——> thilohoffmanni). The feathers of the underparts of thilohoffmanni have very weak pale shaft-streaks (vs. usually fairly marked pale shaft-streaks in rufescens), and the dark subterminal spots of the underparts feathers are mostly shorter, less extensive proximally on the feather than in rufescens (which usually has large squared spots below, offset by slightly paler areas), with a stronger hint of a dark cross-bar near the tip. On the breast and lower throat some markings take the form of short bars or chevrons rather than spots. The tail of thilohoffmanni is more rufous, with nearly equal-width dark and rufous bands (vs. dark brown in rufescens with narrow, widely spaced pale bars). The bases of the inner rectrices and most of the other rectrices of thilohoffmanni are largely black (vs. brown and like the rest of the tail in rufescens). The tarsi of thilohoffmanni are less than half-feathered (vs. almost entirely feathered in rufescens). The podotheca (skin of the toes) of thilohoffmanni is smooth on its uppersurface, whilst that of rufescens is rougher and more heavily D. H. Warakagoda & P C. Rasmussen 94 Bull. B.O.C. 2004 124(2) TABLE 2 Results of factor analyses of external measurements of O. thilohoffmanni with (a) only O. rufescens (see Fig. 2a) and with (b) several other species (see Fig. 2b). Variable abbreviations as in Table 1. a b Variable PC | loadings PC 2 loadings PC3 loadings PC 1 loadings PC 2 loadings Culmen | from cere -0.32 0.22 0.85 0.76 0.54 Maxillad at cere -0.39 -0.78 0.46 0.74 0.34 Rictal bristle | 0.97 0.03 0.05 -0.75 0.62 Auricular | 0.83 -0.05 -0.02 --- --- Ear-tuft | -0.65 0.70 0.06 0.77 0.26 Wing | 0.62 0.32 0.61 -0.47 0.8 Tail | -0.12 0.95 -0).09 --- --- Tarsus | 0.65 0.23 0.11 --- --- Variance explained Salis) 2a IES) Heil) LS) Percent of variance explained 39.33 27.36 16.89 50.09 31.74 t-square for thilohoffmanni 6.86 --- --- 0.09 --- Probability for thilohoffmanni 0.26 =-- --- 0.96 --- armoured. The general feather texture of thilohoffmanni is softer and fluffier (vs. stiffer and harsher in rufescens). In overall size and structure, thilohoffmanni is similar to rufescens (Table 1) but slightly smaller and more delicately built, with a longer wing, a longer but weaker tarsus, and a slightly longer digit 2 (the longest toe). In a principal components analysis (PCA) of external measures (Table 2a, Fig. 2a) in which only thilohoffmanni and rufescens were included, the two were separated on PC-1, which was primarily a contrast axis between longer facial bristles, wing length, and tarsus length vs. longer ear-tufts. PC-2 was significant but did not separate the two species, as specimens of rufescens showed wide variance on this axis. However, in a PCA that included external measures of several species of similar owls (Table 2b, Fig. 2b), thilohoffmanni was very similar both to continental spilocephalus and to balli, and separated only weakly from alfredi and rufescens. In this model, PC-1 was primarily a contrast axis between bill size and ear-tuft length vs. facial bristle length and wing length, and thilohoffmanni is essentially intermediate in these characters between rufescens vs. all the other included taxa. In a PCA of skeletal measurements (Tables 3-4, Fig. 2c), rufescens is the largest species (though differences are slight), spilocephalus the smallest, and thilohoff- manni very like larger individuals of spilocephalus. Shape contrasts did not separate the species for the variables measured. Wing shape was measured as shortfalls of each primary from the longest primary in the folded wing (Fig. 3), and this showed that thilohoffmanni has a very similar wing shape to rufescens; the latter may have a slightly broader inner wing but the samples are too small to be certain. Based on a single specimen, O. icterorhynchus shows a similar wing shape to the above species. Members of the O. magicus superspecies (shown here are the Seychelles Scops-owl O. insularis and the Flores subspecies of Moluccan Scops- D. H. Warakagoda & PC. Rasmussen 95 Bull. B.O.C. 2004 124(2) 50 @— ©. thilohoffmanni (n=1) Ss. @ -—O ©. rufescens (n=6-10) F S iin 40 -—---+ ©. insularis (n=6) ee \ E -.-. O.magicus 5 2 € alviventris (n=15-22) \ aaa = ase la v 30 O. icterorhynchus (n=1) ¢ J \ : | ( \ Qa ‘| ; ad 20 N S \ “wer. \ a. oa \ 10 » Kitulgala PR j \ Eratna - ‘ » Gilimate PR Morapitiya - / Runakanda PR \g_ Sinharaja FR \ ‘ feiss 5S 6 7 8 9 10 \ ®\ Kanneliya FR | Feagee Primary Number aad Fig. 3. Wing shape (as measured by shortfalls of | Fig. 4. Map of Sri Lanka, showing rainforest tracts each primary from folded wingtip) of type from which O. thilohoffmanni has thus far been specimen of Otus thilohoffjmanni, compared recorded. Dashed line shows inland limits of wet with O. rufescens and selected other species of zone. Largest rainforest tract is divided into the scops-owls (mean values shown where n>1). western, smaller portion Morapitiya-Runakanda PR. Data for O. insularis and O. magicus albiventris and the larger, more eastern portion Sinharaja F.R. are from Rasmussen (1998). owl O. magicus albiventris) have markedly narrower inner wings (data for other taxa in Rasmussen 1998 and Lambert & Rasmussen 1998). Distribution Otus thilohoffmanni is endemic to Sri Lanka. It has thus far been found only in lowland rainforests of the south-west quarter of the island within an altitu- dinal range of 30-530 m (Fig. 4). As of January 2004, the species had been detected in Kitulgala PR. (06°59’N, 80°24’E, c.150 m a.s.l.), Sinharaja F.R. (06°25’N, 80°26’E, c.500 m a.s.1.), Morapitiya-Runakanda P.R. (06°29’N, 80°18°E, c.100 m a.s.l.), Kanneliya ER. (06°11’N, 80°22’E, c.30 m a.s.l.) and Eratna-Gilimale P.R. (06°45’°N, 80°26’E, c.100 m a.s.1.). Description of the holotype (colours from Smithe 1975) Crown rounded, lacking differentiated ear-tufts, colour closest to Raw Sienna (136), each feather with several short, narrow Dark Grayish Brown (20) bars across centre. Forehead and supercilium Cinnamon (30) marked with similar short bars as for crown, the supercilium slightly paler than forehead. Circumorbital area and ear-coverts between Raw Sienna and Chestnut (32), with weak, narrow darker barring overall. Ear-covert feathers lack darker, compact distal ends (e.g. a well-formed facial disk border is lacking) and they also lack elongated feather shafts. Rictal bristles fairly long and abundant, and similar in colour to ear-coverts. Nape slightly paler than Bull. B.O.C. 2004 124(2) 96 D. H. Warakagoda & PC. Rasmussen TABLE 3 Skeletal measurements (in mm) of type specimen of O. thilohoffmanni and similar species. L = length, h = height, w = width, d = depth. Species See © a l= 2a = z ao a ee Sake ad ety vee pe Speteeee Pe Senqcgeee See oa en ce Be gee BY ae oe Be wee Po Ce ower ee ee OS ae) Boe AOE Sse ene See Se Soe se SS VE aogece Oisied: tote 5 a, Ae & OF Sts 2 os 3 S 2 17a as & 5 = as) as) = = oy = 3 Oe = : Pe ee SS 8 eo. ts SENS 8 ee ae thilohoffmanni Ree) SO) S037 se. Zile Te Saale 66 8.2 S57] De =): Oren ees - 197 ale eres Sea rufescens RW Sue AtOmemes One) SO10) 9 2200n il ROMm2no) a wikOue Sime 08 BGR me2OW SS Seemeat 20 Sut Smee oe SD QSomn OOO MO2 emOnA Os) O04" COZ e em lor RO 2Ge 2 Os. 0) [eS OMe OLO)/ 0,20 OPO en O40) (n) QB 2 2) OQ Cie) @) VQ) 2) CO Or aor!) Mey 2) 2) @) icterorhynchus eee SO SG) 254m wees Ay Be OGuene Soe eee side 222. 19.3) eR 3 Sy 53 SD --- wee --- an (h.) ee |, 1.44 0.14 0.07 0.78 0 0.21 0.15 (n) G3) (2) C2) Qe) @) ©) & spilocephalus [Or eee se DO meOled kG SIMO emA(top wide OP mmeeno, Oe. eDOM ede | 18S ile S16 9237 SD OP OS Ol WA WER Oe ee CR OPS 22 OA) OI Ohib 1S Ohi) IO Oe OIG (hese (n) oO © OC O CO OOO oo & oO Oo © © © © 8 © © © Scapular proximal w Scapular shaft w D. H. Warakagoda & PC. Rasmussen 97 Bull. B.O.C. 2004 124(2) TABLE 4 Results of factor analyses of skeletal measurements of O. thilohoffmanni, O. rufescens and O. spilocephalus (see Fig. 2c). Variable abbreviations as in Table 3. Variable PC | loadings PC 2 loadings PC 3 loadings Preorbital roof w 0.80 -().48 0.13 Postorbital roof w 0.81 -().49 0.10 Preorbital rim h 0.84 -0).47 0.01 Skull | (w/o maxilla) 0.87 -(0).25 0.37 Max skull w 0.88 0.27 0.32 Max skull h 0.84 0.31 -0.21 Supraorbital process w 0.85 -0).49 0.10 Humerus | 0.74 0.12 0.58 Humerus distal w 0.88 0.29 0.19 Humerus head + deltoid crest w 0.35 0.74 -0).53 Humerus head w/o deltoid crest w 0.91 0.19 -().32 Femur | 0.51 0.73 0.35 Femur proximal w 0.67 0.62 -(0).29 Femur shaft w 0.67 0.3 -(0).28 Coracoid | 0.95 0.001 0.15 Coracoid shaft w 0.68 -0).39 -0).46 Procoracoid + head w 0.71 -0).48 -(0).46 Scapular | 0.97 -0).02 0.05 Scapular proximal w -().25 0.78 0.33 Scapular shaft w 0.62 0.55 -0.13 Variance explained 11.66 4.20 195 Percent of variance explained 58.30 20.99 9.64 t-square for thilohoffmanni 5.45 --- --- Probability for thilohoffmanni 0.37 --- --- crown and similarly marked. Mantle same colour or slightly more rufescent than crown, the markings darker but more widely spaced. Lower back and rump have weaker, more closely spaced dark bars than mantle. Scapulars Cinnamon with weak, widely spaced dark bars, each with a stronger small dark subterminal mark; edges and tips of each scapular more rufous, closer to Tawny than Cinnamon. Secondary-coverts Antique Brown (37) with very fine pale shaft-streaks and tiny dark spots along the shaft; greater coverts close to Cinnamon with larger, blacker shaft-spots. Alula mottled Antique Brown and Cinnamon on outer webs and extreme tips, grading to Dusky Brown (19) on inner webs. Greater primary-coverts Dusky Brown except for Cinnamon on extreme tips. Outer webs and tips of primar- ies and secondaries moderately banded with even-width dark and pale bands of Raw Sienna bounded on both sides by narrow Dark Brownish Olive (129) bars, alternat- ing with pale bands between Cinnamon and Buff; these grade on inner webs to Dusky Brown. Upper tail surface Raw Sienna, weakly and incompletely banded Dusky Brown, the bands stronger on outer webs of outer rectrices, the inner webs and basal portions of each rectrix predominantly Dusky Brown. Throat Cinnamon D. H. Warakagoda & P. C. Rasmussen 98 Bull. B.O.C. 2004 124(2) Bm KHz po SBC 0.5 (b) Fig. 5a—c. Sonograms of territorial songs of (a) O. thilohofjmanni (recorded by DHW), (b) O. rufescens (recording from Malaysia, by J. T. Marshall, from recording in Marshall 1978), and (c) O. spilocephalus (recorded by Pratap Singh, in Himachal Pradesh, north-west India). with very fine, weak darker shaft-streaks. Breast between Tawny (38) and Cinnamon, with short, narrow, Dark Grayish Brown chevrons overall, larger and more triangular on lower breast. Flanks Cinnamon with triangular Dark Grayish Brown spots overall. Centre of belly between Buff (124) and Cinnamon, and essentially unmarked. Tarsal feathering covers less than half the tarsus and is unmarked Cinnamon, slightly darker on front of tarsus and paler, almost whitish, in rear and near distal edge of feathering. Bill wholly pale, laterally compressed, and not sharply curved, with a rather long hooked tip. Tarsi, toes and claws weak, slender, elongate, and entirely pale. Specimens Only the holotype is known. Measurements of the holotype (in mm) Total length (crown to tail tip) c.165, culmen (from cere) 12.9, wing 129, tail 63, tarsus 27.7 (see also Table 1). Voice The song of Otus thilohoffmanni (Fig. 5a) is unobtrusive and easily overlooked. It is diagnostic to species when known but so simple in form and so infrequently delivered that it is easy to understand how the existence of the bird was overlooked until recently. In the forest the song has a ventriloquial quality. The female gives a short, piping, musical, tremulous note pU’U’u that rises slightly and falls again in pitch, identical notes being uttered in series but each note separated by a considerable pause (frequency of recording by DHW 0.65—0.8 kHz, note length 0.3 seconds, repeated after 15—29 seconds). The male gives a slightly lower pitched, slightly shorter, less tremulous version (frequency of recording by DHW D. H. Warakagoda & PC. Rasmussen 99 Bull. B.O.C. 2004 124(2) 0.55—0.7 kHz, note length 0.2 seconds, repeated after 22—35 seconds). Despite its unobtrusiveness, the song of O. thilohoffmanni is distinctive and diagnostic. It resembles that of O. rufescens (Fig. 5b) more than any other regional scops-owl species; however, the song of the latter is louder, longer, more piping, higher pitched, and less quavering, and the differences are consistent with treatment as separate species. The song of O. spilocephalus (Fig. 5c) is an oft-repeated pair of monotonous, short, more bell-like notes, whilst that of O. alfredi is still unknown (suggesting that its song must be inconspicuous or atypical for an owl). Etymology We name the new owl in honour of Mr Thilo W. Hoffmann, who has for so long done much for nature conservation and ornithology in Sri Lanka. Mr Hoffmann was almost single-handedly responsible for saving from destruction the Sinharaja forest, where the owl was first observed. We chose for the species the common name Serendib Scops-owl, which has already appeared informally in some other publications. ‘Serendib’ (also rendered ‘Serendip’) is an ancient name for Sri Lanka. It is the word from which ‘Ceylon’ and a variety of other words were derived, including the English word ‘serendipity’, which aptly describes the unexpected and happy discovery of this new owl. Remarks Habitat and ecology Otus thilohoffmanni has thus far been located only in larger tracts of lowland rainforest, at 30-530 m. All of the localities in which the bird has been observed so far have been disturbed areas with dense, tall secondary growth. The owl appears to be generally rare but common very locally at certain sites. Otus thilohoffmanni is essentially a nocturnal forest bird of secretive habits. However, it usually commences vocalising at dusk, remaining at its roost until darkness falls. Then it starts flying around exploring for food in the vicinity, vocalising for some time while doing this. It nearly always roosts near the ground (sometimes as low as c.1 m), judging from the position of calls at dusk and one observation. The bird’s coloration, size and shape camouflage it very well among clumps of drying or dry leaves, or dead fallen leaves, in dense undergrowth consist- ing of bamboo, viz. Davidsea attenuata, Ochlandra_ stridula_ and Pseudoxythenanthera monadelpha, tree ferns Cyathea spp., other ferns, creepers and other such vegetation, and it has been observed roosting in such a place. It keeps to cover at all times. From observations it appears that a pair maintains a territory year-round. Vocalisations are more frequent in localities with higher densities of the species. It appears from the distribution of vocalisation types heard and one direct observation that the male and female roost apart. Our observations suggest that for about the first two hours after dark O. thilohoffmanni hunts for prey in the undergrowth. It has been seen capturing and consuming beetles and moths, and analysis of stomach contents of the type specimen revealed the partly digested legs, head and elytra of three beetles Bull. B.O.C. 2004 124(2) 100 D. H. Warakagoda & PC. Rasmussen TABLE 5 Qualitative osteological characters of type specimen of O. thilohoffmanni and other Otus species. L = length, w = width, h = height. Species/species groups that share characters with or are very similar to thilohoffmanni indicated in boldface type. Characters Species n Interorbital =Supra- Post- _—Post- Temporal Lateral Angle Cranial —_Lateral Humerus —_Bicipital Coracoid Scapula — Sternal roof w orbital orbital orbital groove production ofotic flange § rimof shaft crest keel h (anterior vs. process process process —_bridge ofexternal capsule ofotic preorbital _— distal lateral posterior) | W direction rim of otic external capsule expansion — expansion capsule vs. vs. (relative to postorbital — internal rest of process rims shaft) thilohoffmanni | much inter- very much unbridged less angle much moderately very little very very weakest, partial narrower mediate broad more produced very thinner inflated _ slightly expanded slender _— slender _shallowest caudally shallow expanded rufescens J} much rather very somewhat nearly to less angle much most slightly little fairly very weak, narrower long, broad more very narrowly produced shallow thinner inflated expanded expanded slender slender __ shallow spiky caudally bridged spilocephalus 5 much small fairly somewhat nearly to less angle much moderately slightly little fairly very weakest, narrower broad more very narrowly produced shallow thinner inflated expanded expanded _— slender _— slender _shallowest caudally bridged bakkamoena several much very long, fairly _slightly nearly to more angle —_ thin, moderately moderately _ little to fairly somewhat slightly sensu lato narrower — spiky broad more broadly produced shallow somewhat inflated expanded moderately slender _— thicker ~~— to much (usually) anteriorly bridged variable expanded deeper icterorhynchus | full, much small much more unbridged more angle = --- inflated moderately moderately heavier _fatrly moderately 2 partial narrower less anteriorly produced —_ very expanded expanded slender deep broad deep SCOps several — equal- small much more broadly much angle thick not moderately moderately _ fairly slightly moderately width less anteriorly bridged more moderate inflated expanded expanded slender thicker deep broad produced — to deep rutilus 4 equal- small much = --- narrowly more angle thick inflated expanded moderately heavier = --- - width less broad bridged produced deep expanded insularis l equal- --- - “- = more angle thick not = -- heavier = --- shallow partial — width produced deep inflated flammeolus several equal- small much — much very much angle thick not moderately _ little heavier very relatively width less more broadly more shallow inflated expanded expanded slender very deep broad anteriorly ~—_ bridged produced Megascops spp. several equal- small less slightly to moderately much angle thick slightly broadly moderately —_ fairly slightly to robust, spp. width broad distinctly —_to broadly more moderate inflated expanded to broadly slender _— distinctly very deep more bridged produced — to deep expanded to heavier thicker anteriorly D. H. Warakagoda & PC. Rasmussen 101 Bull. B.O.C. 2004 124(2) (Scarabaeidae), which had been consumed on the night of capture. The species is able to exploit this feeding niche of the forest during this time, as it then has no nocturnal bird as a competitor. The sympatric nocturnal Ceylon Frogmouth Batrachostomus moniliger, which hunts the same food, roosts as low but flies to higher levels to feed. The sympatric, partially diurnal, endemic Chestnut-backed Owlet Glaucidium castanonotum hunts at low levels in daylight and higher levels nocturnally. Both these species probably become the new owl’s competitors later in the night, when it begins to explore higher levels for the same prey. When O. thilohoffmanni hunts in the undergrowth it often perches easily on thin angled and vertical twigs and stems of plants, the most readily available perches at this level. The small, weak legs and toes may be an adaptation for this light-bodied bird to use such perches. After feeding at this level it usually flies somewhat higher to rest, sometimes for a prolonged period, on a branch that is horizontal or nearly so. When resting it often assumes a ‘relaxed’ position, which is a rather hunched posture with eyes partially closed and feathers somewhat fluffed. After resting it resumes feeding, now at a higher level, between the undergrowth and subcanopy. Its vocal activity peaks again during the last two hours before dawn. In rainforests of the wet zone O. thilohoffmanni replaces the Indian Scops-owl O. bakkamoena. The latter avoids wet forests and occurs in wooded habitats outside these, even around human dwellings. Compared with the two forest species mentioned above, other nocturnal birds occurring sympatrically with O. thilohoff- manni are rare in this habitat. These are: Bay Owl Phodilus badius assimilis, Forest Eagle-owl Bubo nipalensis, Brown Fish-owl Bubo zeylonensis, Brown Wood-owl Strix leptogrammica, Brown Hawk-owl Ninox scutulata and Jungle Nightjar Caprimulgus indicus. Amongst these the Bay Owl also exploits the same levels of forest vegetation and may be encountered hunting for the same prey, but its diet is broader, and the species appears to be much rarer. Brown Hawk-owl is another possible competitor, but it is quite local and rare in Sri Lankan rainforests, and it is sympatric to a much greater degree with the Indian Scops-owl. The other three owls seek larger prey, and the nightjar explores the high canopy in its brief hunting forays to the forest. Systematic relationships Although Otus thilohoffmanni lacks ear-tufts, we initially believed it to be a member of the genus Otus (sensu lato) based on its general appearance and obvious resemblance to O. rufescens. Nevertheless, we could not readily detect external characters diagnostic of the large, highly variable genus Otus, even when restricted to the Old World members, now recognised as generi- cally distinct from most New World members, which have been separated by recent authorities as Megascops. However, we were able to confirm the allocation of O. thilohoffmanni to the subfamily Striginae (which contains mainly the ear-tufted genera Otus and Bubo and their close relatives, and the non-tufted Strix) as opposed to the Surniinae (in which most non-tufted owls fall, including, among small owls, the genera Glaucidium, Athene, and Ninox) by the lack of a triangular dorsal D. H. Warakagoda & P C. Rasmussen 102 Bull. B.O.C. 2004 124(2) process on the jugal bar. Presence or absence of this process is considered diagnos- tic to subfamily within the Strigidae (Ford 1967), and observations during our study are consistent with Ford’s conclusions regarding this osteological character. Although O. rufescens seems to be the most similar species to thilohoffmanni in external appearance, numerous differences exist that suggested the relationship might not be particularly close or the resemblances might even be convergent. These include the very different upperparts pattern, the different facial disk structure, and major differences in ear-tuft development, bill shape, and tarsal and foot characteristics. Otus spilocephalus, despite its many plumage differences even in the extreme rufous morph, is however more similar in certain external structural characters to thilohoffmanni than is rufescens, such as the pattern of the upperparts, its soft plumage and well-developed facial bristles, its weak, unarmoured toes, a similar wing-banding pattern, and its tendency to have blackish bases to the flight feathers (but much less markedly so than in thilohoffmanni). Osteological comparisons (Table 5) further confirmed the correct generic placement of O. thilohoffmanni. Further study is needed of more material to enable reconstruction of the phylogenetic relationships of thilohoffmanni, but based on overall similarity and lack of significant differences, we are now confident that it is indeed closely related to rufescens, and may be its sister species. However, most of these osteological similarities are also shared with O. spilocephalus (and probably with other similar taxa for which skeletal specimens are not available, such as O. balli and O. alfredi), and in external and skeletal proportions, thilohoffmanni is more like these taxa than any are to rufescens. All other groups of scops-owls (for which skeletons were available) differ in several osteological characters from thilohoffmanni, rufescens and spilocephalus. Thus the question of the sister taxon to thilohoffmanni may not be resolvable until DNA-based phylogenetic analyses can be carried out. We are planning such studies but are greatly hampered in this by the lack of material for most of the related taxa and the scarcity of museum specimens, especially recent ones. We can, however, state with confidence that O. thilohoff- manni is one of the more distinctive bird species endemic to Sri Lanka, and that it must have had a fairly long separate evolutionary history on the island. The juvenile (mesoptile) plumage of O. thilohoffmanni remains unknown. That of O. rufescens (based on an NNM specimen) is almost uniform rich rufescent brown, with a weakly defined dark facial disk rim, and very vague, almost obsolete dark barring, strongest on the hindcrown and upper mantle. However, the juvenile (mesoptile) plumage of rufous-morph continental races of spilocephalus is more heavily but still vaguely barred dark and pale over its generally rufous downy plumage. Thus, the juvenile of rwfescens resembles the adult of thilohoffmanni even more strongly than does the adult (except for the downy texture of its plumage), and the juvenile plumage of thilohoffmanni may well be similar to that of one of these species. D. H. Warakagoda & PC. Rasmussen 103 Bull. B.O.C. 2004 124(2) Conservation As of January 2004 c.45 individuals of Otus thilohoffmanni are known from the five sites listed above, each of which is one of Sri Lanka’s few large remaining rainforests. Each is a protected area administered as a Forest Reserve (F.R.) or Proposed Reserve (P.R.) by the Forest Department of Sri Lanka. The species apparently requires a large, fairly intact area of rainforest of a certain size and richness, yet to be quantified and accurately described. It has not been found in rainforests smaller than 8.2 km* in extent. A number of such remnant patches are scattered in the wet zone, and several of these were unsuccessfully surveyed by DHW and colleagues. Of the forests where the species is so far known to occur, its strongholds are the Sinharaja and Morapitiya-Runakanda reserves, which are contiguous and may be considered as effectively one tract. We believe there are more individuals of O. thilohofjmanni living in these five forests than the 45 detected so far. However, from the data gathered the species occupies a quite restricted range within Sri Lanka. The total extent of these five forests is c.230 km’. This can be considered the extent of occurrence of the species as known so far. The initial survey has now investigated c.60% of wet-zone forests out of a total area of such forests estimated at c.2,200 km’ in 1995 (Legg & Jewell 1995). Based on present knowledge we would therefore propose for O. thilohoff- manni the IUCN Red List Category ‘Endangered’ (EN), as it meets criteria B.1.a, B.1.b, B.2.a and B.2.b (and possibly also C.2.a and D) (IUCN 2001). It has long been believed that the composition of the avifauna of Sri Lanka is well known compared to that of other Asian countries. In 1951 W. W. A. Phillips, one of the foremost authorities on the island’s avifauna and a resident of Sri Lanka for three decades, stated that it was ‘most improbable that a bird entirely new to science could now exist in Ceylon’ (as the country was known then) (Spittel 1951). Indeed, very few bird species new to science have been discovered anywhere in South Asia in the past few decades; the others are the morphologically cryptic Nepal Wren-babbler Pnoepyga immaculata, which had previously been collected but not recognised as distinct until its vocalisations were studied (Martens & Eck 1991); the enigmatic Sillem’s Mountain-finch Leucosticte sillemi, still known only from two specimens collected in 1929 and not recognised as distinct for many years (Roselaar 1992); and the Nicobar Scops-owl Otus alius, which was first collected in 1966 but misidentified as O. sunia, then attributed to (but not formally described as) a race of the widespread O. magicus, until it was recognised and described as a full species (Rasmussen 1998). Thus, Otus thilohoffmanni is unique among the birds of South Asia in having been totally overlooked by collectors and other field naturalists alike until its discovery by DHW on the basis of its unfamiliar vocalisa- tions. Acknowledgements We sincerely thank all of the following: the relevant officials and Research Committees of the Department of Wildlife Conservation, in particular Mr A. P. A. Gunasekera and Mr P. C. M. B. Herath., Directors-General, and Mr H. D. Ratnayake, Deputy Director for Research & Education, and of the Forest Department, in particular Mr M. P. A. U. Sarath Fernando, Conservator-General, and Mr D. P. D. H. Warakagoda & PC. Rasmussen 104 Bull. B.O.C. 2004 124(2) Dominique, Assistant Conservator, who provided permissions and assistance to conduct the preliminary field work and survey, to collect the type specimen, and to lend it to PCR for study and museum compar- isons. The relevant officials and staff of the American Museum of Natural History (AMNH), New York; National Museum, Colombo; Museum of Vertebrate Zoology, University of California, Berkeley (MVZ); The Natural History Museum, Tring, UK (BMNH); National Museum of Natural History, Leiden (NNM); National Museum of Natural History, Smithsonian Institution, Washington, D.C. (USNM): University of Michigan Museum of Zoology, Ann Arbor (UMMZ); and Zoological Museum of Amsterdam (ZMA) permitted access to and loan of specimens. The Smithsonian Institution, Mr John Deppman, Mr T. W. Hoffmann, Mr Gunter Lamsfuss, A. Baur & Co. Ltd., Sunbird Ltd., Mr Lester Perera, Dr R. Rudran, Mr Nigel Redman, Ms Dorothy Parker, Mr Peter Landry and Mrs Jo Ann and Mr Hue McKenzie provided funds and equipment to the study project. Mr Jonathan Eames facilitated initial liaison between DHW and PCR; Mr Azim Ghouse and Ms Shirani Johnpillai of Computer Systems International Ltd. provided electronic scans of photographs of the new species; Mr Pratap Singh provided a tape-recording of Otus spilocephalus reproduced here as a sonogram; Mr Jagath Gunawardana advised on legalities; the Ceylon Bird Club acted as the collaborating institution in the study project; Brigadier S. T. Abeyratne helped with information on relevant areas; Mr K. D. Thandula Jayarathna provided additional information from Sinharaja FR; Mr D. Gunadasa offered accommoda- tion for our work in Morapitiya-Runakanda P.R.; Dr S. Kodikara dissected the type specimen and extracted samples of blood and tissue; Mr Gamini Kumara Vithana, Taxidermist, Mrs Chamalka Kothalawala, Assistant Taxidermist, and their staff at the National Museum, Colombo, prepared the type specimen and determined its sex; Mr Lakshman Weeratunga, Curator of Entomology, National Museum, Colombo, identified insects in the stomach of the type specimen; and Mr Suranjan Fernando suggested the proposal in this paper of IUCN Red List status for the new species, and provided relevant literature. We thank especially Dr Pathmanath Samaraweera for his four accurate and beautiful paintings that serve as a frontispiece to this paper; our colleagues in the study project, Messrs Chandima Kahandawala, Kithsiri Gunawardena, Nanda Senanayake, and Niran Caldera for their time, assistance and encourage- ment given so generously in many ways, that made it a success; and Mr Udaya Sirivardana for his extraordinary contributions to the study project and publications relating to the new species. References: Ford, N. 1967. A systematic study of the owls based on comparative osteology. Ph.D. dissertation. Univ. of Michigan, Ann Arbor, MI. 3 IUCN. 2001. JUCN Red List categories and criteria: version 3.1. (UCN Species Survival Commission, Gland & Cambridge, UK. Konig, C., Weick, F. & Becking, J.-H. 1999. Owls: a guide to the owls of the world. Yale Univ. Press, New Haven. Lambert, F. R. & Rasmussen, P. C. 1998. A new scops owl from Sangihe Island, Indonesia. Bull. Brit. Orn. Cl. 118: 204-217. Legg, C. & Jewell, N. 1995. A 1:50,000 scale forest map of Sri Lanka: the basis for a National Forest Geographic Information System. The Sri Lanka Forester, special issue, Remote Sensing: 3—24. Marshall, J. T. 1978. Systematics of smaller Asian night birds based on voice. American Ornithologists’ Union, Washington, D.C. Martens, J. & Eck, S. 1991. Pnoepyga immaculata n. sp., eine neue bodenbewohnende Timalie aus dem Nepal-Himalaya. J. Orn. 32: 179-198. Rasmussen, P. C. 1998. A new scops owl from Great Nicobar Island. Bull. Brit. Orn. Cl. 118: 141-153. Rasmussen, P. C., Schulenberg, T. S., Hawkins, A. F. A. & Voninavoka, R. 2000. Geographic variation in the Malagasy Scops-Owl (Otus rutilus auct.): the existence of an unrecognized species on Madagascar and the taxonomy of other Indian Ocean taxa. Bull. Brit. Orn. Cl. 120: 75-102. Roselaar, C. S. 1992. A new species of mountain finch Leucosticte from western Tibet. Bull. Brit. Orn. G1. 44D5: 225523 18 Smithe, F. B. 1975. Naturalist’s color guide. American Museum of Natural History, New York. Spittel, R. L. (ed.) 1951. Broad-billed Roller story. Loris 6: 326. Warakagoda, D. 2001a. Discovery of a new species of owl in Sri Lanka. Ceylon Bird Club Notes January- February: 1+. D. H. Warakagoda & PC. Rasmussen 105 Bull. B.O.C. 2004 124(2) Warakagoda, D. 2001b. The new species of scops owl in Sri Lanka. Zito 6 (2): 54-59. Warakagoda, D. 2001c. The discovery of Serendib Scops Owl Otus sp. Sri Lanka Naturalist 4 (4): 57-59 Warakagoda, D. 2001d. The discovery of a new owl. Loris 22 (5): 45-47. Warakagoda, D. 200le. Seeking and studying the new owl: the Serendib Scops Owl project in the peri- od July-December 2001. Loris 22 (6): 19-20. White, T. 1984. A field guide to the bird songs of South-East Asia. British Library, National Sound Archive, London. Widodo, W., Cox, J. H. & Rasmussen, P. C. 1999. Rediscovery of the Flores Scops Owl Otus alfredi on Flores, Indonesia, and reaffirmation of its specific status. Forktail 15: 15-23. Addresses: Deepal H. Warakagoda, Ceylon Bird Club, 39, Chatham Street, Colombo 1, Sri Lanka, e- mail: birdclub@sltnet.Ik. Pamela C. Rasmussen, Michigan State University Museum & Department of Zoology, West Circle Drive, East Lansing, MI 48824-1045 USA, e-mail: rasmus39@msu.edu APPENDIX Methods developed during this study for mist-netting and viewing small owls. Movable mist-net method. On 4 August 2001 DHW, Kithsiri Gunawardena and Chandima Kahandawala attempted to capture an individual of O. thilohoffmanni at Morapitiya-Runakanda P.R using mist-nets in the standard manner. Several nets were drawn across posts struck in the ground. They were laid to intercept the bird when flying in different directions within a part of its territory. Each set of nets (across each pair of posts) covered a height of c.1.5—8 m. The owl was coaxed into these by playback of the species’ vocalisation. In several attempts the bird was seen first on one side of a net and soon after on the other, somehow evading it. It was then suggested by Chandima Kahandawala that mist-nets to cover the same height range be set up across two posts not embedded in the ground but each steadied by one person, and the system moved towards the owl sideways along a path while listening to it in the dark (when the bird responded to playback). This method soon proved successful. It was difficult to move the heavy posts used on that occasion and maintain tautness in the nets to prevent their loops around the poles from slipping, while staying silent in darkness. A pair of stiff and strong but light posts in several sections that can be assembled quickly was designed and constructed by Niran Caldera. The height of the nets can be varied before or after the system is set up. The loops engage small projections on the posts. Whilst they do not slide down when the posts are slightly slackened on the move, a net can be lowered quickly by prising the loops off with a light, suitably shaped rod. This system was used on 9 November 2002 at Morapitiya-Runakanda PR. in taking the type specimen and brought success easily. We believe this method will be useful for researchers attempting to capture small owls and other related nightbirds in the dark. Rim method of lighting. Artificial light is essential for nocturnal observations in studying the behaviour of O. thilohoffmanni. In the initial stages of the project it appeared that the bird was discomfited when the brighter centre of the beam of light was directed toward its face for more than several seconds. To avoid this problem, DHW and colleagues began to aim the beam slightly away so that a less bright outer circle of light fell on the bird for prolonged viewing. They observed that the bird then exhibited no discomfort. This was indicated by it reverting to its normal behaviour in chasing after and feeding on insects, flying about normally and perching in its ‘relaxed pose’ after feeding well. The same response was seen in other nocturnal birds observed in forests during the project. We found that the use of artifi- cial light in this manner does not greatly disturb the normal nocturnal activities of nightbirds. © British Ornithologists’ Club 2004 Whittaker et al. 106 Bull. B.O.C. 2004 124(2) First confirmed record of Oilbird Steatornis caripensis for Brazil by Andrew Whittaker, Axel H. Antoine-Feill S. & Robin Schetele Z. Received 14 February 2003 The Oilbird Steatornis caripensis is a rather unusual New World Caprimulgiform and is unique in being the only nocturnal avian frugivore in the world. It occurs locally in montane northern Venezuela, and in the Andes from western Venezuela to western Bolivia, together with the tepuis of southern Venezuela, eastern Colombia, Guyana and Trinidad (Ridgely & Greenfield 2001). Oilbirds are gregarious, with colonies occupying large dark caves, which are used both as daytime roosts and for breeding. They depart the caves at dusk, flying long distances to forage gregariously for fruit, apparently locating aromatic fruit by smell and non-aromatic fruits such as palms by sight (Snow 1962). Recent genetic analysis of Caprimulgiformes indicates that Oilbirds were the earliest to branch away from all lineages (Brumfield et al. 1997), with the species’ closest affinities thought to be with Nyctibiidae (potoos) and Caprimulgidae (nightjars). The distinct rufous plumage and bold white spotting of the Oilbird cause it to resemble superfi- cially the much smaller Rufous Potoo Nyctibius bracteatus. On 21 May 1998 at Palmari Lodge, rio Javari, Amazonas (04°17’S, 70°17’ W) the freshly dead remains of an Oilbird were found by A. Antoine-Feill S. and R. Scheiele Z., along a forest trail through virgin terra firme. Feather samples were collected and five feathers, a primary, two secondaries, one rectrix and a mantle feather, were deposited in the Instituto Nacional de Pesquisa da Amazonia, Manaus (INPA 447) as material evidence for this, the first confirmed Brazilian record. AW made a direct comparison of the Palmari feathers with two Venezuelan specimens at the Museu Emilio Goeldi in Belém (MPEG 33147-48) from the rio Paragua, Cerro Urutani, Bolivar. This confirmed beyond doubt that the feathers belonged to an Oilbird. Following the discovery at Palmari, communication with local inhabitants revealed that they not only knew of the presence locally of Oilbirds, they also described the birds’ plumage, habits and characteristic screaming calls. Furthermore, they informed how Oilbirds are sometimes killed on river cliffs or hollow trees, as they roost by day, later being used as torches by the community as they burn well for long periods. Historically, nestlings were collected by indigenous peoples and cooked to extract a clear, odourless oil that was used mostly for cooking or in some localities for lighting (del Hoyo et al. 1999). From adjacent Peru, D. Graham (pers. comm.) has reported a recent observation of a lone Oilbird. At 2100 h on 1 January 2002 at Paucarillo Forest Reserve, Loreto (03°41’S, 72°11’°W), along the rio Orosa, DG and eight other ornithologists observed an Oilbird at close quarters. The bird was observed in flight by means of Whittaker et al. 107 Bull. B.O.C. 2004 124(2) a strong spotlight beam in which it became disoriented, whereupon it flew towards the light and started to emit strong clicking sounds while it briefly flew in tight circles. The bird remained in the beam, 10—15 m above the riverbank, for c.45 seconds before flying strongly away. This Amazonian locality is c.225 km west- northwest from Palmari and on the south bank of the Amazon. Sick (1984) was the first to report the possibility of Oilbird penetrating Brazilian territory, from occupied caves he located in 1970, in southern Venezuela close to the Brazilian frontier. During the mid 1980s, several colonies were discov- ered in the Venezuelan state of Bolivar, including a huge colony at Aguapira with as many as 10,000 birds. Sick (1993) included Oilbird as occurring in northern Brazil, in Roraima, because the Cerro Urutani has been known to hold an active Oilbird colony since 1978. The cave entrance is 228 m from Brazilian territory (Dickerman & Phelps 1982). However, no sight or specimen records were available confirming the occurrence of Oilbirds in Brazil. Given this, it was highly likely that the species would be confirmed from northern Brazil, most probably from the highlands of Roraima. It was surprising, therefore, to have discovered it in the lowlands of western Amazonian Brazil. The recent Amazonian lowland records from Brazil and Peru, in May and January, together with the comments of the local community around Palmari, strongly suggest that these occurrences in the lowlands may not refer to transitory individuals and that the species may prove be more widespread in Amazonia. The nearest known breeding colony to Palmari in Colombia is c.600 km to the north-northwest in the tablelands of Vaupés (Olivares 1964, Hilty & Brown 1986). Colonies in Peru (T. Schulenberg pers. comm.) are mostly from Andean foothills 800—900 km away, but a recent record from Tahuayo (08°01°S, 74°02’W), c.600 km distant, is the closest record, east across the rio Ucayali. Roca (1994), using radio telemetry in Venezuela on ten Oilbirds, recorded the maximum nocturnal foraging range as 150 km, although one bird moved 240 km in a single night to another roosting cave, demonstrating that the species can cover long distances quickly. It has also been recorded as a vagrant from Tobago, Panama and Costa Rica (Cleere 1998). We suggest that further field work in western Amazonian Brazil and adjacent Peru should aim to locate Oilbirds and confirm their status. This might reveal whether the records reported here involved an unknown lowland colony. If a breeding population does exist, we strongly recommend that new specimens and tissue samples be collected, and a thorough comparison of these materials be made with highland birds in order to evaluate whether these birds represent a new taxon. Acknowledgements We thank T. S. Schulenberg and D. Graham for sharing their knowledge and unpublished data. The manuscript was enhanced by comments and suggestions by Nigel Cleere and Chris Feare, to whom we are very grateful. Maria L. Videira at the Museum Emilio Goeldi, Belém, permitted AW to examine Oilbird specimens held in the collection. AW also acknowledges the wonderful hospitality provided by Palmari Lodge. Whittaker et al. 108 Bull. B.O.C. 2004 124(2) References: Brumfield, R. T., Swofford, D. L. & Braun M. J. 1997. Evolutionary relationships among the potoos (Nyctibiidae) based on isozymes. Pp. 129-145 in Remsen, J. V. (ed.) Studies in Neotropical ornithol- ogy honoring Ted Parker. Orn. Monogr. No. 48. Cleere, N. 1998. Nightjars. A guide to the nightjars and related nightbirds. Pica Press, Robertsbridge. Dickerman, R. W. & Phelps, W. H. 1982. An annotated list of the birds of Cerro Urutani, on the border of Estado Bolivar, Venezuela and Territorio Roraima, Brazil. Amer. Mus. Novit. 273: 1-20. Hilty, S. L. & Brown W. L. 1986. A guide to the birds of Colombia. Princeton Univ. Press. del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 1999. Handbook of the birds of the world, vol. 5. Lynx Edicions, Barcelona. Olivares, A. 1964. Adiciones a las aves de la Comisaria del Vaupés (Colombia), II. Caldasia 9: 379-393. Roca, R. L. 1994. Oilbirds of Venezuela: ecology and conservation. Publ. Nuttall Orn. Cl. 24. Cambridge, MA. Ridgely, R. S. & Greenfield, P. J. 2001. The birds of Ecuador. Cornell Univ. Press, Ithaca, NY. Sick, H. 1993. Birds in Brazil: a natural history. Princeton Univ. Press. Snow, D. W. 1962. Natural history of the Oilbird Steatornis caripensis, in Trinidad, WI. Part II. Population, breeding, ecology and food. Zoologica 47: 199-221. Addresses: Andrew Whittaker, Conjunto Acarigara, Rua Samaumas 214, Manaus 69085-410, Amazonas, Brazil, e-mail: andrew@birdingbraziltours.com. Axel H. Antoine-Feill S. & Robin Scheiele Z., Apartado Aéreo (POB) 94438, Bogota D.C., Colombia. © British Ornithologists’ Club 2004 Rapid speciation by a Lesser Antillean endemic, Barbados Bullfinch Loxigilla barbadensis by R.A. Buckley & Francine G. Buckley Received 9 Fune 2003 The small endemic West Indian emberizine known as the Lesser Antillean Bullfinch Loxigilla noctis is widespread in the Leeward and Windward Lesser Antilles (Fig. 1). It has usually been regarded as highly polytypic and nine subspecies are currently recognised (Table 1). With one exception, all are strongly sexually dichro- matic: males are jet black with rufous throats, rufous or black undertail-coverts, and black bills; females are brownish-olive, paler ventrally, with horn-coloured bills. The exception is the population found only on the isolated and geologically discrete island of Barbados. Originally described by Cory (1886) as a separate species, Barbados Bullfinch Loxigilla barbadensis, nearly all subsequent workers, hewing to 20th-century taxonomic practice, have treated it as another subspecies of the Lesser Antillean Bullfinch, its scientific name then becoming Loxigilla noctis barbadensis. However, the bullfinches resident on Barbados differ in one striking way from the other eight named populations of the Lesser Antillean Bullfinch: they exhibit no sexual dichromatism. In the light of recent treatments of other allopatric West Indian bird populations, reconsideration of the taxonomic status of barbaden- sis 1S warranted. PA. Buckley & Francine G. Buckley 109 Bull. B.O.C. 2004 124(2) Background Until the mid 1980s, essentially the only examinations of Lesser Antillean Bullfinch’s biology concerned its taxonomy (Hellmayr 1938, Bond 1956). Then, Bird (1983) compared the behaviour and ecology of barbadensis with that of several other Lesser Antillean Bullfinches, especially St Lucia’s sclateri and St Vincent’s crissalis, the two geographically closest to barbadensis. Regrettably, no portion of that thesis has ever been published and, despite intense efforts, we have been unable to contact its author. It nonetheless remains a seminal work bearing on the taxonomic status of barbadensis. Equally important information concerns the geological history and age of Barbados. Here, too, the picture has now been clarified, and Barbados’s striking geological history and youth, especially its relationship to islands in the main Lesser Antillean arc, are now well understood. The third piece of the puzzle finally fell into place with publication of a recent analysis of the molecular genetics of Barbados’s breeding landbirds, including barbadensis. Geology, vegetative cover and climate Barbados is unique among the Lesser Antilles in being both very young and lacking any history of volcanism. It is also 150 km east of the main Windward Island chain, well out in the trade winds. Owing to its geological origins, it is relatively low in relief, its highest point, Mt Hillaby, reaching only 335 m, with about two-thirds of the island ranging from sea level to c.100 m, and almost another third to c.200 m. Whereas basal rocks in north-eastern Barbados have been dated to the Upper Eocene/Tertiary (50-70 My BP), these are crustal rocks pushed up as a tectonic mound along the Barbados Ridge. This feature originated (and is still rising) as the South American Plate slid west-northwestward under the Caribbean Plate, in the process heating crust that emerged as lava from volcanoes on the Lesser Antillean Ridge from Grenada to Saba, along the main Lesser Antillean arc. These present- day islands first appeared in the Miocene, 15—30 My BP, and are still rising (Speed 1988, Perfit & Williams 1989, Speed & Keller 1993). Their volcanic soils were doubtless vegetated quickly, so they would have had a long history of avian coloni- sation and evolution. *Proto-Barbados’ on the other hand only emerged in fits and starts at the end of the Pleistocene, c.700,000—1 My BP, and for much of its early history was a combination of coral reefs and low-lying small islands, periodically eroded, submerged and rebuilt in response to sea-level changes, oceanic and rainwater erosion, and sedimentation. On average, it has been rising c.0.3 m per 1,000 years. The best evidence (Mesolella 1967) suggests that the core of present-day Barbados emerged 600—700,000 y BP. Originally a circular dome (the centre of the uplift), perhaps two-thirds of this original island subsequently eroded away; then c.300,000 y BP, a new island arose to its south-west (near present-day Bridgetown), eventually fusing via crustal uplift with the now much smaller main island. PA. Buckley & Francine G. Buckley 110 Bull. B.O.C. 2004 124(2) Forest vegetation was probably slow to accumulate in such a low-relief, dynamic environment, and though there are as yet no known dates for establishment, forests most probably followed on the merging of Proto-Barbados and Christ Church islands, i.e. up to 300,000 y BP. Limestone soil generated by erosion (and, eventu- ally, plant growth) was augmented by episodic infusions of volcanic ash from neighbouring St Lucia and St Vincent (e.g. an estimated 3.25 million tonnes [76 tonnes/ha] fell on Barbados following the irruption of St Vincent’s Soufriére Volcano in 1901: Gooding 1974). Many plants probably colonised Barbados from the south (but not the north or west) via ocean currents such as the Antilles Current, fed by waters draining the Amazon and Orinoco Rivers and even western Africa. Winds doubtless also brought plant propagules from South America (Urania moths still regularly arrive on Barbados with southerly winds, as do vagrant and colonis- ing birds), from West Africa, the source of airborne sediments as well as Desert Locusts Schistocerca gregaria (Prospero 1968, Rainey 1989, Savoie et al. 1989), and also from the Lesser Antilles north of Barbados. Birds might still be contribut- ing plant material and seeds from North America, the West Indies and South America in soil on their feet and in their excreta. One analysis (Gooding 1974) estimated that of 478 extant, non-introduced, higher plant species on Barbados, 12% came from the north, 19% came from northern South America, 43% occurred throughout the Caribbean/tropical continental America, and 26% were pantropical; only five (1%) were Barbados endemics. By the time of European colonisation in the early 1600s, Barbados was covered in forest, but unlike the volcanic Antillean-arc forests, 1t was not tropical rain forest, nor was it widespread. The high centre of the island, with good soil and 2,030 mm per year of rainfall, did support a rich mesic tropical hardwood woodland, whilst lower and drier elevations averaging 1,520 mm per year and sea coasts with only 1,015 mm per year grew only poorer hardwood and dry scrub forests, respectively. Especially on the windward side of Barbados, woody vegetation was conspicuously stunted and wind-shaped by salt spray. Although persistent east—north-easterly trade winds blow at 15—30 kph most of the year, Barbados’s low relief has eliminated most orographic precipitation, so the island is relatively dry: its mean annual rainfall of 520 mm is only about half that of St Lucia, whose tall mountains (nine in excess of 610 m, the highest 950 m) and strikingly vertical, montane topography (10% of St Lucia lies above 365 m) extract much more moisture from trade winds. Accordingly, St Lucia’s tall, lush, and highly diverse tropical rain forests and elfin woodlands are wholly lacking on Barbados. This is reflected in endemic avian species: Barbados currently has but one (a few others were probably extirpated shortly after European colonisation: Hutt ef al. in press), whilst St Lucia has three (perhaps four), including two endemic genera (Keith 1997). Geographic variation within Lesser Antillean Bullfinches Nine subspecies of Loxigilla noctis have been described (Table 1), many on only minor differences in colour, patterning or (not shown) measurements. All but one PA. Buckley & Francine G. Buckley 111 Bull. B.O.C. 2004 124(2) TABLE | Subspecies of Lesser Antillean Bullfinch Loxigilla noctis (from north to south), their occurrence, and their male coloration (from Ridgway 1901) Islands Taxon Male plumage Anguilla, St Martin, ridgwayi head and upper breast matte black, fading to ashy black St Barthelemy, Barbuda, on rump, belly and tail; rufous-chestnut supraloral Antigua spot, chin, throat and undertail-coverts; black bill Saba, St Eustatius, St Kitts, = coryi jet black, with rufous-chestnut supraloral spot, chin, Nevis, Montserrat throat and undertail-coverts, black bill Guadeloupe, Iles des Saintes, dominicana jet black, with rufous-chestnut supraloral spot, chin, Marie-Galante, Dominica throat and undertail-coverts, black bill Désirade desiradensis head and upper breast matte black, fading to ashy black on rump, belly and tail; rufous-chestnut supraloral spot, chin, throat and undertail-coverts; black bill Martinique noctis jet black, with rufous-chestnut supraloral spot, chin and throat, black undertail-coverts, black bill St Lucia sclateri jet black, with rufous-chestnut supraloral spot, chin and throat, black undertail-coverts, black bill Barbados barbadensis as female: brownish olive dorsally, grey ventrally, with orange-rufous undertail-coverts, dusky-horn bill St Vincent crissalis jet black, with rufous-chestnut supraloral spot, chin, throat and undertail-coverts, black bill Grenada grenadensis jet black, with rufous-chestnut supraloral spot, chin, throat and undertail-coverts, black bill are strongly sexually dichromatic: black-billed males are jet black (or, on shrubby, xeric islands, black fading to ashy black posteriorly), with rufous-chestnut supralo- ral spots, chins, throats and undertail-coverts (Fig. 1). Two taxa have wholly black undertail-coverts, and individuals in a few others sometimes show black feathers intermingled with rufous. Females vary in more subtle ways through the Lesser Antilles and not always concordantly with males. This local differentiation indicates that the Lesser Antillean Bullfinch is morphologically labile, probably in response to environmental conditions. Such eco-typical adaptation in plumage colour is hardly unknown in birds, so its appear- ance in the West Indies is unsurprising, even if its manifestation on islands only 10 km apart might be (jet black dominicana on Guadeloupe vs. ashy-black desiraden- sis on Désirade). Analysis of similar inter-island variation in Darwin’s Finches (Geospizinae; Grant 1986) suggests that Lesser Antillean Bullfinch variation probably has a genetic basis. However variable, all Lesser Antillean Bullfinch populations still maintain strong sexual dichromatism—except barbadensis (Fig. 2), which has uniquely become sexually monochromatic, males and females PA. Buckley & Francine G. Buckley 112 Bull. B.O.C. 2004 124(2) ‘+Gledeloupe i et Désirade Mare 6 Soe 4 =) Isles aes 7 Sia Saintes ; = Martinique eee CARIBBEAN SEA Figure 1. The West Indies, indicating all islands supporting forms of Lesser Antillean Bullfinch Loxigilla noctis, sensu lato, discussed in this paper. resembling females of all other populations, a condition also called ‘hen-feathering’ (Mayr 1942). In addition, we were immediately struck by how different Lesser Antillean Bullfinches were on Barbados and St Lucia, hen-feathering aside. Where sclateri is a solitary, generally shy, usually within-vegetation forager, barbadensis is a bold, open-country and woodland, ground-feeder that often occurs in small feeding groups with Black-faced Grassquits Tiaris bicolor, especially during the dry season. The question immediately posing itself is whether morphological, ecological and behavioural changes in barbadensis have been accompanied by changes in its biological-species status, because we suspect that this unique switch from sexual dichromatism to sexual monochromatism was a profound, not trivial, evolutionary step. Results Ecology and behaviour of Barbados and St Lucia bullfinches Bird (1983) questioned whether the change in morphology in barbadensis was attended by parallel behavioural and ecological changes and, if so, how these might be explained in terms of selective pressures and evolutionary history. Although she was not especially concerned with taxonomy, her results nonetheless have taxonomic implications. She compared barbadensis to its nearest geographic (and PA. Buckley & Francine G. Buckley L Bull. B.O.C. 2004 124(2) Figure 2. Male Lesser Antillean Bullfinch Loxigilla noctis sclateri from St Lucia, Lesser Antilles (Wayne Arendt) Figure 3. Male Barbados Bullfinch Loxigilla barbadensis (P. A. Buckley) P. A. Buckley & Francine G. Buckley 114 TABLE 2 Bull. B.O.C. 2004 124(2) Ecological and morphological comparison of the resident forms of 'Lesser Antillean Bullfinch' on Barbados (barbadensis) and St. Lucia (sclateri); data adapted from Bird (1983) and Ridgway (1901). All quantitative differences mentioned are statistically significant; see text and (Bird 1983) for additional information. Character Male plumage Female plumage Diet fruit flowers seeds insects Foraging behaviour pecking insect gleaning foot-holding flower-base chewing nectar-feeding ground-feeding frequency foraging between 1-12 m modal foraging height mean foraging height Breeding biology male nest-building effort (as % of female's) mean incubation bout length mean non-incubation interval mean times male feeds incubating female male nestling feeding trips/hr female nestling feeding trips/hr mean time male at nest/feeding trip mean time female at nest/feeding trip response to nest predators advertising/courtship displays/vocalisations barbadensis brownish olive dorsally, grey ventrally with orange- rufous undertail-coverts: dusky-horn lower mandible brownish olive dorsally, grey ventrally with orangish undertail-coverts; pale horn lower mandible 10% 29% 36% 20% 59.5% 13.0% 11.0% 10.0% 4.5% 50% 49% Om 24m 114.0 25.7 min 6.9 min 9.0 15 7 38.5 sec 58.6 sec attack, vocalise undescribed time males spent within 3 m of nest during AM: nest building incubation brood rearing 22-30% 28-46% 14-22% sclateri jet black with rufous- chestnut throat and pre- orbital spot; bill glossy black brownish olive dorsally, grey ventrally with orangish undertail-coverts; pale horn lower mandible 32% 40% 10% 8% 45.5% 7.5% 27.5% 4.0% 14.5% 2% 92% 4-5m 6.6m 60.5 56.6 min 14.6 min 3.7 cA 1.0 77.4 sec 101.7 sec flee, remain silent undescribed 46% 46% 4% PA. Buckley & Francine G. Buckley 115 Bull. B.O.C. 2004 124(2) mean intruder chases by males/2-hr period during: nest building 8.0 2.0 incubation 16.0 1.7 brood-rearing 13.7 2.0 mean number of male 'songs'/2-hour period during: nest building 9.7 5 we incubation 14.0 1.0 brood rearing 7.0 20 dichromatic) neighbours, St Lucia’s sclateri and St Vincent’s crissalis, seeking insight into the geographic source of Barbados birds. Because we now know that barbadensis colonisers came from St Lucia and not St Vincent (see below), for the purposes of this paper we will only compare her findings for sclateri and barbaden- sis (in Table 2); readers are referred to Bird (1983) for additional information. All quantitative comparisons discussed here were statistically significant (P = 0.05). DIET Proportional diet composition differed strikingly between the islands. Seeds obtained on the ground and from flower heads accounted for 65% of barbadensis’s diet, but nearly that same fraction of sclateri’s came from fruit and flowers. Conversely, barbadensis consumed only c.10% fruit, sclateri only 8% seeds. (Diet composition as a function of food-type availability was not examined on either island.) Differences in wet—dry season diet composition were statistically signifi- cant on Barbados (much more fruit in the wet season, more seeds in the dry) but perhaps unsurprisingly were not on St Vincent (the wet island surrogate for St Lucia, from where Bird was unable to obtain dietary data). FORAGING BEHAVIOUR Unsurprisingly, the two populations’ different diets were obtained in different fashions: barbadensis spent fully half its time feeding on the ground, which sclateri almost never did; barbadensis foraged only half the time at 1-12 m, where sclateri foraged nearly exclusively. Correspondingly, feeding postures and gleaning techniques also differed (Table 2). In the dry season barbadensis increased seed eating, insect eating and ground foraging (the latter almost doubling); dry-season foraging data were unavailable for sclateri. Data on flock sizes were not collected, as sclateri is essentially solitary, and barbadensis more gregarious although not properly ‘flocking’. NEST BUILDING, PARENTAL CARE AND AGGRESSION The most obvious difference between barbadensis and all other Lesser Antillean Bullfinches is male coloration. Not unexpectedly, relatively cryptically coloured male barbadensis behaved quite differently from non-cryptic sclateri. Male P. A. Buckley & Francine G. Buckley 116 Bull. B.O.C. 2004 124(2) TABLE 3 Results of MANOVA contrasting seven sclateri and barbadensis measurements (mm) of males: wing chord, tail, tarsal width, exposed culmen, bill width @ proximal end of nares, middle-toe claw, and hind-toe claw. MANOVA pairwise comparisons shown for the only two features differing significantly (bill width and tarsal thickness). Variable Mean Std Err Lambda F df P bill width barbadensis 5.500 0.129 4.127 ve de | 1,14 .0616 sclateri 5.083 0.154 tarsal thickness barbadensis 2.850 0.076 13.443 13.443 1,14 .0025 sclateri 2.417 0.083 Omnibus MANOVA Value F df P Wilks's Lambda 0.788 AD Sil 7,8 0.0301 barbadensis expended more than twice as much nest-building effort as sclateri and fed incubating females twice as frequently, and their incubation bouts were only half as long as those of sclateri, as were their inter-incubation intervals. Once young hatched, male barbadensis made 50% more feeding trips per unit time, and females 70% more, than sclateri. Conversely, both male and female barbadensis spent only about half the time at the nest during each feeding bout than did sclateri males and females. Cryptically coloured male barbadensis remained in the vicinity of their nests five times longer than did sclateri from nest building through brood rearing; were strikingly (4-8 times) more likely to chase intruders (especially during incubation); and ‘sang’ 3—14 times more frequently than did sclateri males. Aggression towards conspecifics was not significantly different under high and low densities on Barbados, but was higher than on St Lucia (sclateri), where bullfinch densities in ‘semi-residential lowlands’ were essentially identical to those of barbadensis. Categorical responses to both avian (especially Green Heron Butorides virescens, TABLE 4 Results of mtDNA analyses sequencing 842 bp of overlapping ATPase-6 and ATPase-8 genes in haplotypes of barbadensis and sclateri. Cf. Lovette et al. (1999) for additional information. Variable barbadensis sclateri Sample size 21 36 Range of pairwise nucleotide differences within 0-2 l=] Range of pairwise nucleotide differences between - 3-7 Minimum pairwise divergence between - 0.36% PA. Buckley & Francine G. Buckley 117 Bull. B.O.C. 2004 124(2) Broad-winged Hawk Buteo platypterus, American Kestrel Falco sparverius, Carib Grackle Quiscalus lugubris, Grey Kingbird Tyrannus dominicensis, Tropical Mockingbird Mimus gilvus) and non-avian (typically Anolis spp., domestic cat Felis sylvestris) predators on various islands were even more dramatic: male barbaden- sis generally aggressively attacked and vocalised, when male sc/ateri remained completely silent and/or fled. Body architecture Structural differences between male barbadensis and sclateri are not immediately obvious, but our own measurements of males of both taxa in the collections of the Museum of Comparative Zoology (MCZ), Cambridge, Massachusetts, USA, revealed that barbadensis males had almost 50% thicker (stouter) tarsometatarsi and 10% broader bills than sclateri males. Overall, males of the two populations differed significantly when all measurements were analysed using multivariate techniques (Table 3), although these results may signify only multivariate mean differences, not individual diagnosability. Bird (1983) measured several structural variables in barbadensis and sclateri, searching for sexual as well as population differences. Two measures of bill length (exposed culmen, nares to tip) were inconclusive or contradictory, owing perhaps to small sample sizes, although she did demonstrate that bill depth, flattened wing and tail lengths of both barbadensis and sclateri males exceeded those of females. She also measured ‘tarsal length’ but in two ways that were not so unequivocally described as to allow confident replication. The first she called ‘tarsus 1: length of tarsometatarsus, and the second ‘tarsus 2: distance from proximal end of tarsometatarsus to distal margin of last undivided scute.’ ‘Tarsus 2’ (which she believed ‘accurate only to 2 mm’) would seem the conventional tarsus measurement but she did not so state, despite citing Baldwin et al. (1931). Moreover, she referred to ‘tarsus 1’ as ‘length of tarsus,’ a term Baldwin et a/. (1931) would restrict to her ‘tarsus 2.’ In any case, she failed to find sexual differences in either barbadensis or sclateri using ‘tarsus 2” measurements, but did with ‘tarsus 1.’ Finally, although she did compare ‘tarsus 1’ and ‘tarsus 2’ measurements for male and for female barbadensis to male and to female sclateri, respectively, she presented no raw data or sample sizes, opting for a table that nonetheless indicated that by both methods barbadensis had highly significantly longer tarsi than sclateri. Mitochondrial DNA Lovette et al. (1999) analysed mtDNA from eight resident passerines on Barbados, among them Lesser Antillean Bullfinches from Barbados (barbadensis), St Lucia (sclateri), and St Vincent (crissalis), to ascertain patterns and timing of colonisation on Barbados. Initially the entire 894—bp mtDNA genomes for ATPase 6 and ATPase 8 for five barbadensis and sclateri were sequenced to confirm and characterise inter-island differentiation, followed for an additional 21 barbadensis and 32 scla- teri by either Restriction Fragment Length Polymorphism (RFLP) digestion of PA. Buckley & Francine G. Buckley 118 Bull. B.O.C. 2004 124(2) PCR-amplified products, or by additional sequencing. To examine individual island monophyly, enzyme cleavage and RFLP gels were compared among islands, and sample sizes used (Table 4) were regarded as adequate for detection of low-frequen- cy haplotypes. They found (1) no evidence of any founder-effect on the three islands; (2) only a single clade of lineages on each of the three islands (i.e., recip- rocal monophyly between islands); (3) that the three taxa had accumulated 3—5 sub- stitutions among the three islands; (4) that although barbadensis and crissalis had 0.60% nucleotide divergence, barbadensis and sclateri differed by only 0.36%, implying St Lucia to be Barbados’s source population; and (5) assuming a uniform molecular clock, consistently low levels of mtDNA differentiation on Barbados indicating relatively recent colonisation events by at least four species, the Lesser Antillean Bullfinch among them. Discussion Bird’s (1983) ecological and behavioural data demonstrate that barbadensis differs from sclateri in diet (particularly during Barbados’s stressful dry season, to which it seems well adapted), foraging behaviour, nest attentiveness, and aggression. At all stages in its breeding cycle, barbadensis biology is in many respects (including overall coloration but excluding sexual dichromatism) more like that of a grassquit Tiaris spp. than all other Lesser Antillean Bullfinches. Granivory and insectivory are well-known avian adaptations to xeric environments (Lack 1976), and Barbados is among the driest of Lesser Antillean islands. Food pressures are greatest in dry seasons, when both insects and seeds are more buffered from immediate climatic vicissitudes than is fruit, so facultative granivory/insectivory assumes high selective value under such conditions. Ground foraging is obviously associated with granivory, and pale and/or cryptic coloration is another classic avian adaptation for terrestrial foraging. This is not to say that barbadensis is not an arboreal forager or frugivore; it most certainly is during the wet season, as one would expect of a generalist. Higher feeding rates of barbadensis males are probably a function of the low energy content of small seeds, and increased feeding in turn leads to more frequent encounters with conspecifics, etc. There are no resident hawks or owls on Barbados, so such predation pressure on adults as now exists probably comes largely from feral quadrupeds and perhaps grackles. Even though these were surely unimportant in the evolution of barbadensis monochromatism, it remains wholly conjectural what might have been. There have been occasional references in the literature to partially or wholly black male bullfinches on Barbados (e.g. Hellmayr 1938, Bird 1983), usually attrib- uted to new St Lucia or St Vincent immigrants or to residual ancestral variation within barbadensis. We believe that, owing to the distance between St Lucia and Barbados and prevailing easterly trade winds, it is likely that few if any bullfinches continue to arrive unassisted on Barbados from St Lucia (with no evidence of any ever having arrived from St Vincent). However, this does not preclude occasional PA. Buckley & Francine G. Buckley 119 Bull. B.O.C. 2004 124(2) ship-borne transport by inter-island ferries, although we are also aware of no shipboard observations of Lesser Antillean Bullfinches near Barbados. At any rate, cock-feathered males are excessively rare on Barbados, and several active observers with 120+ years of combined field experience on Barbados (E. B. Massiah, M. D. Frost, the late M. Hutt and the late H. F. Hutt pers. comms.) have never seen or heard of a single one. Whether from natural colonisers, ship-assisted waifs or intra- Barbados recombination, genes of such individuals would quickly be swamped on Barbados. Why has barbadensis diverged so greatly from all other Lesser Antillean Bullfinches? There are several not mutually exclusive possibilities: (1) the potential for eco-typical differentiation within the Lesser Antillean Bullfinch complex is well established (see above); (2) molecular analyses found Barbadian Black-faced Grassquit’s mtDNA nucleotide divergence from St Lucia birds to be 0% (Lovette er al. 1999), indicating recent arrival on Barbados. Thus, in the absence of past competition from its most likely ground-feeding, seed-eating emberizine competi- tor, ‘proto-barbadensis’ could have quickly moved into an important vacant niche; (3) body-structure differences (especially stouter tarsi and wider bills) are clearly associated with, respectively, terrestrial habits and increased seed-eating. (In our own analyses, length of hind claw, another cursorial adaptation, approached statis- tical significance); (4) Barbados is radically different from almost all other Lesser Antillean islands in geological history, soil, climate and vegetation; and, (5) Barbados is sufficiently far east of the main Lesser Antillean arc to preclude repeated reinvasion from source populations. Hellmayr (1938) assumed that monochromatism in barbadensis was a primitive or ancestral condition and that sexual dichromatism in all other Lesser Antillean Bullfinch populations derived from it, but we now know that barbadensis derived from a surely dichromatic St Lucia population, not the reverse. Bird (1983) on the other hand did not specifically address this question, although suspecting (based on a single Barbados male with some blackish body and rufous throat feathers) that the Barbados founding population was dichromatic and thus that barbadensis was secondarily monochromatic. We believe it is taxonomically significant that despite plumage and structural changes within the nine currently recognised Lesser Antillean Bullfinch subspecies, eight have nonetheless retained sexual dichroma- tism. We are unaware of any published studies of the Lesser Antillean Bullfinch nuclear genome (including micro-satellites), so all inferences concerning the age of various populations rely on mtDNA data. These offer several possible sources of error, some of which are amenable to study, some not: (1) it is possible, although quite unlikely, that rare barbadensis haplotypes in sclateri were not detected; (2) the ‘mean rate’ of mtDNA accumulation customarily used for passerines (2% per My) surely varies among genera and species, yet it is exceedingly difficult to calibrate the absolute rate for a single species, or to calculate error terms; (3) the duration of time required for each taxon to complete the biological speciation process is unique; PA. Buckley & Francine G. Buckley 120 Bull. B.O.C. 2004 124(2) (4) statistical separation of small among-species differences in percent nucleotide divergence requires much larger samples than have been available; and, (5) the approach used by Lovette er al. (1999) would fail to detect earlier invasions masked by complete replacement of mtDNA lineages, although the probability of an invading haplotype wholly replacing a resident one would be very small indeed (1/population size). Nonetheless, given that geological data strongly support Barbados’s emergence =700,000 y BP; assuming a molecular clock with a nucleotide substitution rate of 2% per My; accepting that barbadensis is monophyletic in origin; and agreeing that the 0.36% nucleotide substitution divergence between barbadensis and sclateri is approximately correct, we reason, after consideration of the potentially confound- ing factors noted above, that proto-barbadensis probably invaded Barbados from St Lucia sometime 700,000—180,000 y BP—and considerably closer to the latter than the former considering mtDNA data from four Barbados taxa. Although courtship, pair formation and attendant displays (postural and vocal) have never been studied in Loxigilla, we suggest that females choose males and non-randomly, given that female choice is customary in strongly sexually dichro- matic passerines. We further propose that male advertising song plays a major role, as does distinctive male plumage (and thus that sexual selection operates to some degree within the dichromatic species), but that the importance of both has been severely curtailed in sexually monochromatic barbadensis. We further propose that barbadensis females choose their males using behavioural or fitness characters such as frequency of song, aggression toward conspecifics and predators, and frequency and quality of courtship feeding. Finally, we consider that this complex of factors, coupled with other behavioural and ecological features, especially loss of distinctive male plumage, has resulted in barbadensis having diverged so far from noctis stock as to have achieved biological-species status. Collectively these notions offer fertile ground for vocal playback and plumage-alteration experiments designed to elucidate the exact operation and relative roles of isolating mechanisms, whose existence we do not doubt. Peterson (1996) accumulated many instances of geographic variation in avian sexual dichromatism. He determined that whilst variation in coloration of either sex was about equally likely, males were about five times more likely to lose than to gain bright plumage (reflecting initial incidence), and although males of island populations were more likely to lose than gain bright colour, they were not necessar- ily more likely to do so than their continental counterparts. He suggested that sexual dichromatism characters are likely to have a simple Mendelian or sex-linked basis whose alleles may be segregating in wild populations. Granted that plumage aberra- tions in wild birds often follow Mendelian inheritance (reviewed in Buckley 1987), the evidence for widespread Mendelian inheritance of species-specific characters is less strong. Further, Peterson (1996) asserted that loss and/or gain of bright or dull plumage (especially on islands) is more frequently due to genetic drift than to selection. He did acknowledge, though, that loss of bright male plumage might play PA. Buckley & Francine G. Buckley 121 Bull. B.O.C. 2004 124(2) a significant role in biological speciation, although allopatry would prevent the majority of island examples from being tested in nature. Doherty ef al. (2003) considered what effect sexual selection might have on local extinction rates and turnover in avian communities. Extending earlier work indicating that dichromatic waterfowl (Promislow ef al. 1994) and passerines (Promislow ef al. 1992) seemed to suffer higher mortality rates than sexually monochromatic congeners, Doherty ef a/. (2003) modelled 21 years of data from the North American Breeding Bird Survey (BBS), finding that dichromatic species showed a mean 23% increase in annual local extinction rates over monochromatic species per BBS survey route. But they unexpectedly also showed that this increase in local extinction was almost exactly offset by local immigration and recolonisa- tion, leading to relative community stability. Whereas this offset may occur regularly in continental settings, it is demonstrably rare on oceanic islands (MacArthur & Wilson 1967), which may explain the disproportionately large number of monochromatic bird species on such islands. We believe it most likely that ancestors of the present-day West Indian endemic emberizine assemblage (Loxigilla, Melopyrrha, Melanospiza), irrespective of number of invasions, were dichromatic, possibly akin to present-day Volatinia, and that there has been strong stabilising (sexual?) selection to maintain dichromatism. We consider that the plumage, behavioural and structural changes that have occurred in Lesser Antillean Bullfinch populations in general (and Barbados Bullfinch in particular) have a nuclear genetic basis that has been selected for. Therefore, Barbados Bullfinch would show both nuclear and mitochondrial evolution, the package comprising sufficient divergence from the main line of Lesser Antillean Bullfinch evolution as to have developed concomitant prezygotic reproductive isolating mechanisms. Thus, we suggest that the form of ‘Lesser Antillean Bullfinch’ on Barbados is best treated as a separate biological species, Barbados Bullfinch Loxigilla barbadensis Cory 1886, which probably colonised Barbados from St Lucia around 180,000—700,000 y BP, and which has achieved specific status since its arrival. As such this represents one of the more rapid examples of avian speciation, but because this happened in an oceanic island context, it is perhaps less surprising; e.g. Klicka & Zink (1997) have also noted, on the basis of mtDNA chronology, that a few avian species do appear to have arisen unexpectedly rapidly. And what of the low level of mitochondrial nucleotide divergence found by Lovette et al. (1999) for barbadensis? Accepted practice, developed from divergence levels of known species-pairs, indicates that values below c.3% indicate only subspecific differentiation. Yet it is already known that birds may display pronounced, nuclear-genetic-based geographic variation that is not mirrored in mtDNA (e.g. Brawn et al. 1996). We believe Barbados Bullfinch is another example, and suggest that this phenomenon may be more common on oceanic islands than continents. We would also argue that whenever possible, it is better science to infer taxonomic status from non-molecular evidence, and then to use P. A. Buckley & Francine G. Buckley 122 Bull. B.O.C. 2004 124(2) molecular data to derive time since colonisation, hence timing and duration of speciation. Increasingly, genetic and ethological studies are suggesting that island bird populations formerly lumped into polytypic species-complexes can be considered biological species just as parsimoniously. In the West Indies alone, the four endemic Myiarchus flycatchers were split into seven (Lanyon 1967); each of the four allopatric subspecies of ‘Stripe-headed Tanager, Spindalis zena’, is now considered a species (Garrido et al. 1997); each of the three isolated subspecies of “Dendroica adelaidae’ is now considered a species (Adelaide, Barbuda and St Lucia Warblers, respectively; Lovette et al. 1998); the isolated (and still extant?) Puerto Rican Bullfinch Loxigilla portoricensis on St Kitts has just been recognised as St Kitts Bullfinch L. grandis (Garrido & Wiley 2003); and the taxonomic status of the two allopatric Cuban Bullfinch Melopyrrha nigra populations is also under evaluation (J. Wiley, pers. comm.). To this group we now add Barbados Bullfinch. Acknowledgements Our work on the avifauna of Barbados has been supported by the US National Park Service and the US Geological Survey. We thank Douglas Causey and Alison Pirie for access to specimens in the MCZ collections. For hospitality, support and field companionship on Barbados, we are indebted to our Barbados Checklist co-authors: the late Maurice and the late Hazel Hutt, Edward Massiah and Martin Frost. Wayne Arendt kindly supplied the photo of Loxigilla noctis sclateri, and Dennis Skidds, Environmental Data Center, URI, prepared Fig. 1. For discussion of their ongoing work on the deriva- tion of the West Indian avifauna, for reprints and preprints, and for information of various sorts, we thank Eldredege Bermingham, the late Nedra Klein, Irby Lovette, Herbert Raffaele, Robert Ricklefs and James Wiley. And for constructive comments on various versions of this manuscript we acknowledge Chris Feare, Martin Frost, Douglas Futuyma, Allan Keith, Edward Massiah, Michael Patten, Townsend Peterson, Robert Ricklefs and James Wiley. We dedicate this paper to Ernst Mayr on the occasion of his 100th birthday. - References: Baldwin, S., Oberholser H. & Worley, L. 1931. Measurements of birds. Sci. Publ. Cleveland Mus. Nat. Hist. 2: 1-165. Bird, J. 1983. Behavioral and ecological comparisons of Lesser Antillean Bullfinches: a study of the evo- lution of sexual dimorphism and monomorphism. Ph.D. thesis. Univ. of Montana, Missoula. Bond, J. 1956 et seg. Checklist of the birds of the West Indies, fourth edn, and supplements 1—27. 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Part I. Family Fringillidae. Bull. US Natl. Mus. 50: 1-715. Savoie, S., Prospero, J. & Saltzman, E. 1989. Non-sea salt sulfate and nitrate in trade wind aerosols at Barbados: evidence for long-range transport. J. Geophysical Res. 94: 5069-5080. Speed, R. 1988. Geological history of Barbados: a preliminary synthesis. Trans. 11th Carib. Geol. Congr. 29: 1-11. Speed, R. & Keller, C. 1993. Synopsis of the geological evolution of Barbados. J. Barbados Mus. & Historical Soc. 41: 113-139. Addresses: P. A. Buckley, USGS-Patuxent Wildlife Research Center, Box 8 @ Graduate School of Oceanography, University of Rhode Island, Narragansett RI 02882 USA, e-mail: pabuckley@uri.ed. Francine G. Buckley, Dept. of Natural Resource Sciences, Coastal Institute-Kingston, University of Rhode Island, Kingston RI 02881 USA, e-mail: fgb@uri.edu © British Ornithologists’ Club 2004 Willem-Pier Vellinga et al. 124 Bull. B.O.C. 2004 124(2) New and interesting records of birds from Ayabaca province, Piura, north-west Peru by Willem-Pier Vellinga, Fferemy N. M. Flanagan & Todd R. Mark Received 16 fuly 2002; revision received 16 February 2004 Because almost every reasonably-sized remnant humid forest in south-west Ecuador has been recognised as a Key Area for bird conservation in South America (Wege & Long 1995), it is clear that more field work is needed to assess the conser- vation status of areas in adjacent parts of north-west Peru. Some of the northernmost humid forests in this region are in the province of Ayabaca (dpto. Piura). Much field work has been performed in neighbouring Ecuador, within 50—100 km to the north/north-west (e.g. Bloch et al. 1991, Williams & Tobias 1994, Best & Kessler 1995). Approximately 80 km to the south, relatively extensive investigations were conducted, primarily in the 1920s and 1930s (Palambla) and in the 1970s (near Canchaque and Huancabamba) (Parker et al. 1985). Ayabaca has largely escaped such attention, although Best et al. (1993) presented some field data for the region, and additional information is available in Schjellerup (2000). This paper reports on the results of field work in Ayabaca, in 2000, and aims to clarify the conservation status of humid forests in the area. The avifauna of the province is interesting as it represents a transition between several biogeographic regions and Endemic Bird Areas (EBAs). The province straddles parts of three EBAs, Central Andean Paramo (EBA 043), the Tumbesian region (EBA 045) and the Southern Central Andes (EBA 046) (Stattersfield et al. 1998). The latter two are of interest in this study, as will be discussed. The work by Best et a/., which was centred on the Bosque de Cuyas on Cerro Chacas (see below), subsequently led to its inclusion in the Southern Central Andes EBA (046), and to its recognition as a Key Area for bird conservation in South America (Wege & Long 1995), due to the presence of a number of threatened species (Collar et al. 1994). Ayabaca is one of eight provinces that comprise the department of Piura. It is bordered to the north and north-east by Ecuador and to the west, south and south- east by the provinces of Sullana, Piura, Morropon and Huancabamba. Within Piura, Ayabaca and Huancabamba are highland provinces. The altitude of Ayabaca in general rises from 400 m in the west to over 3,000 m in the east. The economy is split broadly between subsistence agriculture in the highlands and rice production and cattle ranching at lower elevations. The capital, the town of Ayabaca (04°38’S, 79°42’W) lies at 2,700 m and is situated on the eastern flank of a mountain that reaches 3,000 m and lies west of the main Andean chain, isolated by a narrow, dry, rainshadow depression, formed by the watershed between the catchments of the rios Calvas and Quiroz (Fig. 1). Natural habitat at all altitudes within the depression Willem-Pier Vellinga et al. 125 Bull. B.O.C. 2004 124(2) PRR 4 ae (2 wit 2 ih AS Pe Roey © * Pt Rae & 5 . Pere phy é 04°40’ 1 04°50’ 80°00" 79°50" 79°40’ 79°30’ 7o720—s VV Figure |. General area of the study sites. A: Ayabaca town, Y: Yanchala, 1: Bosque de Cuyas (with la: Bosque de Cuyas and 1b: Bosque los Molinos), 2: Aypate, 3: El Toldo. The locality indicated by 4 is Huamba, data for which (Schjellerup 2000) have been used in comparison. Heights have been interpo- lated from the GLOBE-DEM dataset, www.ngdc.noaa.gov/seg/topo/globeget.shtml. The map covers parts of Peru and Ecuador, but the political boundary is not indicated. (minimum altitude 2,000 m) is severely degraded by human activities. Various patches of more or less intact forest remain on the slopes east of the depression, which are connected to the main Andean chain by ridges above 2,500 m. Study sites and methods The study focused on three forests at higher altitudes (generally above 2,400 m) of Ayabaca province, one on Cerro Chacas, a mountain isolated from the main Andean chain (Bosque de Cuyas), and two on a spur on the west slope of the main Andean chain (Aypate and El Toldo; see Fig. 1). Aypate is on a somewhat isolated mountain connected to the main Andean chain by a ridge. For each site the coordinates reflect the general area of the sites. Bosque de Cuyas (04°36’S, 79°44’W, 2,200-3,100 m) 29 June—1 July 2000 and 5—9 July 2000. Includes the Key Area of Cerro Chacas (Wege & Long (1995). However, the forest extends from Cerro Chacas, incorporating other cerros and quebradas, so the locally used name Bosque de Cuyas seems more appropriate in describing this location. A neighbouring forest, Bosque Los Molinos, at the head of a Willem-Pier Vellinga et al. 126 Bull. B.O.C. 2004 124(2) the Quebrada Corriente de los Molinos, was visited briefly on two occasions. This forest is connected to Bosque de Cuyas, with Cerro Llantuma (or Yantuma) between them, and the entire area should be considered a single forest. The total area of forest is estimated at 1,000 ha, with Bosque de Cuyas covering 600 ha and Bosque Los Molinos 400 ha. Forest commences at 2,200 m and reaches 2,900 m. Still higher (but over a rather limited area), forest is replaced by patches of elfin forest or tussock grassland grazed by cattle. Although most remaining forest has been modified by man, with timber extraction, and cattle grazing the understorey, patches of primary forest persist on the steepest slopes. Within better-conserved or primary forest, the general profile consists of a tree layer with dominant families such as Lauraceae, Melastomataceae, Myrsanaceae, Clusiaceae, Erythrina spp., Ericaceae and Arecaceae, occasionally reaching 20—30 m tall and diameters of up to 1 m. Below this a scrub or bush layer with dominant Baccharis sp., Vervesina pentantha (Asteraceae), Piperaceae, Solanaceae, Papilionaceae, Amaryllidaceae and Clorantaceae, reaches a maximum height of 6 m, and there is a herbaceous layer with a mix of vines, tree-ferns, orchids such as Epidendrum spp., Lepanthes spp. and Pleurothallis spp., mosses, lichens and bromeliads. Higher paramo vegetation is dominated by stunted communities consisting of Ericaceae (Befaria sp.), Melastomataceae, Myrsanaceae, Rubiaceae, Fabaceae, Amaryllidaceae (Bomarea sp.), Asteraceae (Baccharis sp.), Clusiaceae, Piperaceae, with a mix of bushes and grasses, such as Tibouchina (Baccharis spp.), Lupinus silvestris (Fabaceae), Fuchsia sp. (Onagraceae), Gentiana spp., Halenia spp. (Gentianaceae), as well as various Poaceae (Chusquea sp., Stipa sp.). Secondary forest consists of Amaryllidaceae (Bomarea spp.), Asteraceae (Onoseris sp., Mixania sp., Senecio sp.), Clusiaceae (Clusia sp., Hypericum sp.), Ericaceae (Bejaria sp., Cavendishia sp.), Myrsianaceae (Cybianthus rhopaloides, Myrcine sp.), Solanacea (Jchoma sp.), Piperaceae (Piper spp.), Campanulaceae (Siphocampylus sp.), Cyatheaceae (Cyathea spp.), Droseraceae (Drosera sp.), Gentinaceae (Gentina sp., Halenia sp., Sybolanthus sp.), Melastomaceae (Brachyotum sp., Miconia sp., Tibouchina sp.) and Rubiaceae (Cinchona calisaya, Cinchona sp.). As some 60 ha of Bosque de Cuyas are owned by the Municipal Council of Ayabaca, which is interested to protect the forest and implement a management plan for the area, the authors provided their data on the region. Aypate (04°42’S, 79°35’W, 2,800-3,100 m) 2-4 July 2000. Aypate is known nationally and, to a certain extent, internationally as an important Inca site on the Inca highway between Cusco and Cajamarca. The total forest is estimated to cover 600-800 ha, although locals are clearing new fields. The forest is separated from the Bosque de Cuyas, some 17 km away, by the depression mentioned above (see Fig. 1). However, it is connected to the forests above El Toldo and the main Andean chain by ridges, dotted with native humid shrub and hedges, above 2,500 m. Willem-Pier Vellinga et al. 127 Bull. B.O.C. 2004 124(2) El Toldo (04°40°S, 79°31°W, 2,800—3,100 m) 10-13 July 2000. A number of forest patches exist near this small village. The general area is well known for its archeo- logical interest because of the presence of the Samanga petroglyphs. We visited one forest patch of c.400 ha, two hours walk above the village, at the head of the Quebrada el Toldo. Understorey was degraded by grazing cattle. Other patches of similar size were noted in the vicinity, one of which, above Huamba, has been visited twice by expeditions from the University of San Marcos in Lima (Schjellerup 2000), see Appendix 1. Field work was conducted on 1—13 July 2000 by JMNE, TM and WPY. Intensive, opportunistic birding was complemented by modest mist-netting efforts. Vocalisations were routinely recorded. We were joined by Abundio Segastagui of the Universidad Nacional de Trujillo who studied the flora of the three locations (Segastegui unpubl.). Records of interest Best et al. (1993) mentioned 59 species for Bosque de Cuyas, recorded during seven field observer days. Inevitably, we encountered a number of new species for this forest which, together with several unpublished records (see Acknowledgements), brings the number of species recorded in Bosque de Cuyas to around 110. No records from the other two forests were available previous to our study, during which c.65 species were recorded both at El Toldo and at Aypate. The complete lists of species recorded at each site are presented in Appendix 1. Threat status, where applicable, is taken from BirdLife International (2000): VU = Vulnerable and NT = Near Threatened. BEARDED GUAN Penelope barbata (VU) The species’ presence at Bosque de Cuyas was reconfirmed and moreover its local distribution was determined to extend to Bosque los Molinos. Several were encoun- tered on a daily basis. We also found it at Aypate and El Toldo, new localities for this globally threatened species (BirdLife International 2000, Flanagan er a/. 2000). Although threatened by habitat destruction and hunting, this guan persists for now in small fragments of forest with disturbed understorey. Locals admit to continued hunting of this species (at least in Bosque de Cuyas and El Toldo), which some refer to as ‘pucacunga’ or ‘bare-throat’ in Quechua. OCHRE-BELLIED DOVE Leptotila ochraceiventris (VU) Best et al. (1993) mentioned the only record of this threatened species at Bosque de Cuyas. We failed to relocate the species, and suggest that more tangible evidence of the species’ presence at this locality is required. Willem-Pier Vellinga et al. 128 Bull. B.O.C. 2004 124(2) PARAKEETS 4Aratinga sp. On 9 July a flock of 25-30 Aratinga sp. parakeets was noted flying over the lower section of Bosque de Cuyas, at c.2,200 m. Another flock of c.40 Aratinga sp. was observed flying across the road between Ayabaca and Yanchala at approximately the same elevation. These may have either been Scarlet-fronted Parakeet A. wagleri or Red-masked Parakeet A. erythrogenys. A. wagleri is unknown from the area and is only infrequently recorded in adjacent Ecuador, whilst A. erythrogenys is known from the general area. Although usually encountered at lower altitudes, it has apparently been recorded as high as 2,500 m in Utuana, Ecuador (Ridgely & Greenfield 2001). SCALY-NAPED PARROT Amazona mercenaria Although not recorded during our study, the species has been recorded on several occasions (in July 1998 and November 2000) in Bosque de Cuyas by JNMF. It is not considered resident. The nearest records for the species are from Amaluza, Ecuador (Williams & Tobias 1994) and Cerro Chinguela (Parker et a/. 1985). STYGIAN OWL Asio stygius Three pairs were heard along a 2-km stretch of the main road through Bosque de Cuyas between c.2,200—2,600 m on the evenings of 6—7 July. All were calling from the canopy of mature primary forest. Calls commenced shortly after sunset, and continued throughout the night on 6 July. On 6 July a pair was sound-recorded for 20 minutes giving an antiphonal duet (published in part on Krabbe et a/. (2001). The female was observed once, flying overhead in dense fog, permitting a view of the Buteo-like silhouette and large size. This represents only the second record in Peru, with the first, from around Sallique south of Huancabamba, still unpublished (J.P.O’ Neill pers. comm.) However, the species is known from various localities in adjacent Ecuador: Sozoranga, Angashcola and the Cordillera de Quichiragua (Best & Kessler 1995), and occurrence in Peru is unsurprising. The vocalisation period in Bosque de Cuyas coincides with records from Amaluza (Williams & Tobias 1994), where the species was heard in July/August 1990 and July 1991. In Bosque de Cuyas vocalisations were not heard during visits in October and December 2000, by JNME, nor was there response to playback on those occasions. AMAZILIA SP. We briefly observed an Amazilia sp. in a Eucalyptus tree alongside the main road in Yanchala (2,100 m), which leads through small agricultural fields with hedges of native forest vegetation. The bird was perched c.10 m up. The bill was red or dark orange with a dark, perhaps black, tip. The chin, throat, belly and vent were white or at least very pale. The bird had rufous flanks and the crown was green. Regrettably, the coloration of the upper tail was not visible. The record is interest- ing given recent literature concerning Amazilia taxa in this region. In Weller (2000) and del Hoyo ef al. (1999) Loja Hummingbird A. alticola was split from Amazilia Willem-Pier Vellinga et al. 129 Bull. B.O.C. 2004 124(2) Hummingbird Amazilia amazilia, but in Ridgely & Greenfield (2001) this treatment was not followed because of the existence of an as-yet undescribed form in Azuay, Ecuador. The amount and distribution of pale and rufous coloration on the observed bird accords with characters mentioned for A. (a.) alticola in Weller (2000), del Hoyo et al. (1999) and Ridgely & Greenfield (2001), but it is unclear whether A. a. leucophaea or A. a. dumerilii can be safely eliminated, as the amount of rufous apparently shows appreciable individual variation (Ridgely & Greenfield 2001). The closest locality from which A. (a.) alticola is known is apparently Malacatos, Loja, Ecuador (04°14’°S, 79°15’ W, 1,500 m). It seems to occur sympatrically with A. a. dumerilii in the Casanga Valley in central Loja, Ecuador (04°08’S, 79°49’ W, 900 m). A. a. dumerilii is also known from Cruzpamba (04°10’S, 80°01’ W, 1,000 m) and Paletillas (04°11°S, 80°17’W, 500 m), both in Loja, Ecuador. A. a. leucophaea is known from both lowland localities (north-west to Alamor, Piura, Peru, 04°29’S, 80°25’W, 110 m) and highland localities (north to Palambla, Piura, Peru, 05°23’S, 79°37’ W, 1,200-—2,000 m). The present record is from an area between these localities, where any of the three taxa might in principle occur. Subsequent visits to the area should aim to clarify this matter. SMOKY-BROWN WOODPECKER UVeniliornis fumigatus Rather common at all localities. Of interest 1s the fact that it is unclear which taxon, be it Kv f fumigatus or V f obscuratus, is present, as obscuratus occurs around Huancabamba, Peru, and fumigatus in all Ecuadorian ranges south to Loja, but with those in south-west Ecuador apparently intermediate (Ridgely & Greenfield 2001). The characters of a male mist-netted in Bosque de Cuyas do not closely match either subspecies, although it resembled obscuratus more than fumigatus. It had a pale, whitish face contrasting sharply with the red cap and dark grey malar region. The face was palest on the lores and around the eye. The grey throat was somewhat paler than the malar region but showed no sharp contrast. Belly and mantle had a distinct olive wash, the mantle contrasting with the dark upperwing. Its appearance was rather similar to that shown in Frimer & Moller (1989) from the Cordillera Blanca. RUFOUS-NECKED FOLIAGE-GLEANER Syndactyla ruficollis (VU) This endangered Tumbesian endemic was encountered on several occasions at Bosque de Cuyas, in second growth as well as in more pristine habitat. The forest may prove to be a stronghold for this Vulnerable species. GREY-HEADED ANTBIRD Myrmeciza griseiceps (VU) No efforts were made to find this species and we failed to locate it in July 2000, but it was recorded on a subsequent visit, in December 2000, by JNMF and Rob Williams. The species may be genuinely rare in Bosque de Cuyas. It has been encountered on at least two other occasions (Best et a/. 1993, P. Coopmans pers. comm. ). Willem-Pier Vellinga et al. 130 Bull. B.O.C. 2004 124(2) RUSTY-BREASTED ANTPITTA Grallaricula ferrugineipectus (levmebambae?) Encountered at 2,200 m in Bosque de Cuyas, where it had earlier been found by P. Coopmans. The species only sang early morning. The habitat, of rather sparse understorey, agrees with the literature (Fjeldsa & Krabbe 1990). Long known from the west slope of the Andes in Peru from specimens taken independently by Parker and Koepcke at Canchaque (Parker ef al. 1985), and more recently in Ecuador, at Utuana (P. Coopmans unpubl.), the population is apparently isolated from that on the east slope south to Bolivia, G. f leymebambae. The closest known population of leymebambae appears to be that recently discovered at Cerro Wicsocunga (06°05’S, 78°20’ W), on the north-westernmost spur of the Cordillera Central, above the town of Lonya Grande, dpto. Amazonas (TRM & L. Augustine unpubl.). BLACKISH TAPACULO Scytalopus latrans subcinereus The only Scytalopus at the study sites. Individuals were observed chasing one another uttering excited calls. The reason for such behaviour, which once involved three individuals, is unclear but may have represented a type of territorial behaviour or be related to breeding activity. GOLDEN-CROWNED FLYCATCHER Myiodynastes chrysocephalus (minor?) Twice an adult was observed feeding two fledged young. This rather isolated record appears to be the first west-slope record for Peru. Although not identified to subspecies level, it was probably M. c. minor, which in Ecuador occurs on the west slope south to western Loja, where apparently fairly common in small (<1 ha) woodlots intermixed with fields and plantations at Alamor (03°52’S, 80°05’W), c.110 km from Bosque de Cuyas (Williams & Tobias 1994), and along the east slope as far south as the Cordillera del Condor (Ridgely & Greenfield 2001). The nominate race is broadly distributed, on the east slope, from Peru to Bolivia, but is only known south of the Marafion. This would be the first record of minor in Peru. Apparently unknown on the east slope north of the Marafion in Peru, where it 1s, however, likely to occur. PIURA HEMISPINGUS Aemispingus piurae This distinctive endemic taxon is easily encountered in Bosque de Cuyas, but is apparently absent at the other localities. It was recently suggested to split this taxon at specific level from H. melanotis based on a phylogenetic analysis (Garcia- Moreno et al. 2001). MASKED SALTATOR Saltator cinctus (NT) One above El Toldo perched motionless for c.30 seconds in the open on a thick horizontal branch dotted with mosses and bromeliads, some 10 m above ground. Simultaneously, a typical flock containing Pearled Treerunner Margarornis squamiger, Streaked Tuftedcheek Pseudocolaptes boissoneautii, Blue-capped Tanager Thraupis cyanocephala, Blue-and-black Tanager Tangara vassorii, Brown- Willem-Pier Vellinga et al. 131 Bull. B.O.C. 2004 124(2) capped Vireo Vireo leucophrys, Superciliaried Hemispingus Hemispingus supercil- iaris and Blue-backed Conebill Conirostrum sitticolor was passing through the vicinity. The saltator may have been associated with this flock, although we did not find it again in similar flocks. This is one of the few observations in Peru, although the species was already known to occur in the general area (Schjellerup 2000). It has been suggested that it depends on Chusquea or on Podocarpus cones (BirdLife International 2000). Both vegetation types were present in the forest, but neither was common. NORTHERN RUFOUS-NAPED BRUSH-FINCH Aflapetes latinuchus ssp. The taxa most likely to occur in Ayabaca, A. /. comptus and A. I. latinuchus have recently been treated as subspecies of a single species (Garcia-Moreno & Fjeldsa 1999), and generally characterised by the lack of a black forehead, sharp demarca- tion between the rufous cap and greyish back, long yellow malar stripe, light melanisation on the flanks, and white speculum in several populations. Fjeldsa & Krabbe (1990) and Ridgely & Greenfield (2001) described further distinguishing Figure 2. Two Northern Rufous-naped Brush-finches Atlapetes latinuchus mist-netted together at El Toldo. Note the difference in speculum and extent of the pale nape (Willem-Pier Vellinga) Willem-Pier Vellinga et al. 132 Bull. B.O.C. 2004 124(2) TABLE 1 Distinguishing characters of subspecies of Northern Rufous-naped Brush-finch Atlapetes latinuchus based on Fjeldsa & Krabbe (1991), Garcia-Moreno & Fjeldsa (1999), Ridgely & Greenfield (2001) and specimens in Louisiana State University Museum of Zoology. bd crown speculum — supraloral submalar spot streak A.l.latinuchus chestnut (paler on nape south medium vestigial very faint, of Maranon) or absent variable A.l.spodionotus chestnut never never moderate A.l.chugurensis light chestnut, paler on nape never never very faint A.l.comptus rufous or chestnut in Ecuador: never large (reduced __ distinct usually paler than A./.spodionotus, in some) especially on nape characters of these taxa. These characters and an indication of their variability, based on specimens of A. /atinuchus in the Louisiana State Uuniversity Museum of Zoology, are described in Table 1. In Bosque de Cuyas we encountered birds on which the supraloral spot (never large, never absent) and the submalar streak (usually distinct, sometimes faint) were variable, and on which the nape was distinctly paler than the crown. We never observed a speculum on these birds, neither in the field or in the hand. Similar birds were encountered at Aypate. These brush-finches seemingly possess traits similar to those described for A. /. comptus in Ecuador (for which we lack information on variability in the malar streak). Birds were encountered in a range of habitats, ranging from low scrub and hedges between fields to the undergrowth and canopy of the tallest trees in primary forest. Similar catholic tastes in habitat have been noted for A. /. comptus in the Celica mountains in Ecuador (Bloch et al. 1991). In sharp contrast, birds above El Toldo showed clear variation in the extent of the speculum; all those observed in the field had at least a hint of this and in some it was very obvious. Of two birds caught simultaneously (Fig. 2), one had a speculum consisting of white patches on the base and centre of the seven outermost primaries, whereas the other only showed a hint of a speculum, consisting of a little white on the five outermost primaries. Both had a faint submalar streak and no supraloral spot. The extent of rufous in the crown and nape differed appreciably between them; the crown and nape of that with a speculum extended further onto the back, ending in a squarish shape, as opposed to a more rounded shape in the other. That without a clear speculum resembled A. /. comptus from Ecuador, whereas the other clearly showed characters of both 4. /. latinuchus and A. I. comptus from Ecuador. Comparison of the characters of these birds with those shown in Table 1 shows that they cannot be safely attributed to either currently recognised subspecies. Variation among taxa of A. latinuchus in this region, Willem-Pier Vellinga et al. 133 Bull. B.O.C. 2004 124(2) especially the fact that strikingly different forms occur syntopically, warrants further investigation. Altitudinal extensions PAURAQUE WNyctidromus albicollis The familiar call was recorded at Bosque de Cuyas and Aypate. A pair was mist- netted at Bosque de Cuyas. At Aypate birds were calling and observed flying around our camp near the ruins at 2,800 m. These records are high for the species, the record at Aypate apparently representing an elevational extension of c.500 m over published data (Fjeldsa & Krabbe 1990). ECUADORIAN PICULET Picumnus sclateri One at the lower edge of Bosque de Cuyas, at 1,900 m, was apparently somewhat high. Ridgely & Greenfield (2001) described an altitudinal range of 1,500—1,700 m for the population in Loja, Ecuador, but it has been seen there at nearly 2,000 m (P. Coopmans pers. comm.). CHAPMAN’S ANTSHRIKE Thamnophilus zarumae A Tumbesian encountered daily in and around Bosque de Cuyas, in disturbed as well as pristine habitat. Also recorded at Yanchala, in hedges of native vegetation. Near Ayabaca birds were seen at 2,700 m. It has been recorded as high as 2,500 m at Utuana, Ecuador, and 2,550 m at Amaluza, Ecuador (Ridgely & Greenfield 2001). GREY-BREASTED MARTIN Progze chalybea Fifty were present in Ayabaca town, at 2,700 m, during our entire stay. They were also encountered feeding above Bosque los Molinos. This appears to be a new altitudinal record for the species, which seems to occur to c.2,000 m in southern Ecuador, with one record from 2,570 m (Ridgely & Greenfield 2001). Breeding activity In July 2000 evidence of breeding activity for the following species was obtained. Speckled Hummingbird Adelomyias melanogenis: fledged juvenile apparently being fed by an adult at Bosque de Cuyas. Sparkling Violetear Colibri coruscans: nest building below an overhang beside the road outside Ayabaca to Bosque de Cuyas. Grey-breasted Mountain-toucan Andigena hypoglauca: fledged juvenile accompanied by persistently alarm-calling adults at El Toldo; the juvenile clambered to a height of c.3 m in small trees. Line-cheeked Spinetail Cranioleuca antisiensis: a juvenile mist-netted at Bosque de Cuyas. Ash-coloured Tapaculo Myornis senilis: one in juvenile plumage observed near Aypate. Barred Fruiteater Pipreola arcuata: fledged juvenile accompanied by both adults at El Toldo. Northern Rufous-naped Brush-finch Aftlapetes latinuchus: single fledged Willem-Pier Vellinga et al. 134 Bull. B.O.C. 2004 124(2) juveniles accompanying small groups of adults in low secondary vegetation at El Toldo. Discussion and conclusion The Bosque de Cuyas forms an isolated island of humid montane cloud forest on the eastern fringe of the Tumbesian region, to the west of nearby humid montane cloud forests in the main Andean chain (Fig. 1). Similar forest is still found on a number of isolated mountains above 2,500 m in neighbouring Ecuador: east of Gonzanama (c.04°13’S, 79°24’W), in the Celica range (c.04°03’S, 79°56’W), in the Chilla range (c.03°33’S, 79°15’W), in the Sozoranga range (especially near Utuana (04°22’S, 79°42’W), and near Uritusinga (c.04°06’S, 79°09’ W) (Bloch et al. 1991, Williams & Tobias 1994, Best & Kessler 1995, Ridgely & Greenfield 2001). In Peru, other areas of quite similar humid montane cloud forest exist on the west slope of the western cordillera of the Andes, south of Cerro Chinguela. The best-known such locality is Cruz Blanca (05°20’S, 79°32’W; Parker et al. 1985), but a few others exist south of the Porculla pass in Cajamarca. Southern forests were discussed in Koepcke (1961) and Franke (1992), and more recently the forests at the head of the Zafia Valley (which apparently possess an exceptionally rich avifauna) have been subject to ornithological investigation by teams from the University of San Marcos in Lima (Salinas et al. 1998, 2003). Most such ‘west-slope’ forests in Ecuador, as well as Peru, were included in EBA 046 (Stattersfield et al. 1998), because of the occurrence of the restricted- range endemics Bearded Guan Penelope barbata, Purple-throated Sunangel Heliangelus viola and Rainbow Starfrontlet Coeligena iris. But in fact their avifauna is characteristically different from that of forests within EBA 046 in the main Andean chain, such as those in Podocarpus National Park in Ecuador. For one, the total number of species occurring in west-slope forests is fewer, usually lacking otherwise characteristic birds such as tinamous, jays, mountain-tanagers, toucans, caciques and fruiteaters. The difference is highlighted in a limited comparison between several ‘isolated’ and ‘main Andean chain’ forests in EBA 046, in Appendix 2. Perhaps more notable is the occurrence of a number of endemic taxa character- istic of the highlands of EBA 045 in these EBA 046 forests. Examples include the local form of Rusty-breasted Antpitta Grallaricula ferrugineipectus, Line-cheeked Spinetail Cranioleuca antisiensis, Rufous-necked Foliage-gleaner Syndactyla ruficollis, Chapman’s Antshrike Thamnophilus zarumae, Loja Tyrannulet Zimmerius (chrysops) flavidifrons, Three-banded Warbler Basileuterus trifasciatus, Piura Hemispingus Hemispingus piurae and Black-cowled Saltator Saltator nigriceps. These striking differences are easily appreciated when one travels the short distance from Ayabaca across the Calvas—Quiréz watershed. During our relatively brief forays to Aypate and El Toldo we readily found c.20 species that have so far Willem-Pier Vellinga et al. 135 Bull. B.O.C. 2004 124(2) never been encountered in Bosque de Cuyas. In Huamba another 20 species have been noted that do not reach Bosque de Cuyas (Schjellerup 2000). Conversely, several species were encountered in Bosque de Cuyas but not at the other two locations, or in Huamba. For now, we cannot exclude that these differences are not the result of undersampling, given that Bosque de Cuyas has been subject to relatively far greater ornithological investigation. Still, we note that some of the common Tumbesian endemic taxa of Bosque the Cuyas are at least much scarcer or perhaps absent at Aypate, El Toldo and Huamba, e.g. Hemispingus piurae, Zimmerius (chrysops) flavidifrons, Thamnophilus zarumae, Syndactyla ruficollis and Basileuterus trifasciatus. The total area of EBA 046 is estimated at 10,000 km’ (Stattersfield et a/. 1998). Regarding total forest cover in the area, Best et al. (1993) stated (with some caveats) that “humid to very humid montane cloud forest’ is “found throughout south-west Ecuador above 2.000 m’. However forests away from the main Andean chain, as discussed above, are actually quite rare; Gonzanama: ‘only a tiny fragment [a few ha] of heavily disturbed, mainly secondary forest remaining’; Uritusinga: ‘one patch of relatively good forest” (a few km*); Sozoranga: ‘the small and isolated mountain top of Jatunpampa’, ‘only small forest patches left’; the Celica range: two localities mentioned, one of 400 ha, the other of 300 ha. In Ridgely & Greenfield (2001) the area of remnant forest and woodland near Utuana is specifically mentioned as being of great importance. Part of the Utuana forest is currently protected, with as much as 1,000 ha targeted for future conservation by the Arcoiris and Jocotoco founda- tions. In Ridgely & Greenfield (2001) the distinctive character and avifauna of these montane west-slope forests and their peculiar conservation situation were highlighted, by splitting the Tumbesian EBA (045) into lowland (“Tumbesian lowlands’) and highland (“Southwestern highlands’) sectors. It was stated that such “separation’ might also prove useful in Peru. This indeed seems to be true. Including the very similar Peruvian forests within the “Tumbesian highlands’ might well be more appropriate. It is clear from a comparison of a number of such Tumbesian highland forests (Appendix 2) that Bosque de Cuyas is of conservation importance. Fourteen distinctive, range-restricted taxa have been recorded there. Three globally threat- ened species occur (all listed as Vulnerable in BirdLife International 2000): Bearded Guan, Grey-headed Antbird and Rufous-necked Foliage-Gleaner, and it is certainly important for the guan and foliage-gleaner. Additionally, the occurrence of Stygian Owl and the local form of Rusty-breasted Antpitta is notable. The forests near El Toldo and Aypate are also interesting from a conservation standpoint, in particular given the presence of two Near-Threatened species: Grey- breasted Mountain-toucan and Masked Saltator (BirdLife International 2000). Other forests of ornithological and conservation importance undoubtedly await discovery in Ayabaca province. Several, possibly similar to that above El Toldo, were indeed noticed from a distance during our field work. Conceivably, remnants Willem-Pier Vellinga et al. 136 Bull. B.O.C. 2004 124(2) of forest similar to Bosque de Cuyas may persist on the slopes above Frias. Furthermore, humid forests at lower elevations might hold populations of other of the Tumbesian endemics. Whether any important lower altitude humid forest is extant in Ayabaca province or neighbouring provinces is unknown. It is most probable that, at least in the higher reaches of the Cerros de Amotape, important populations of some Tumbesian endemics will be located. The first expedition patroned by ProAves Peru to this ornithologically uncharted territory was made in June 2000 (Whiffin & Sadgrove 2000) and, more recently, a ProAves Peru project was launched to study forests along the Loja/Ayabaca border, between Peru and Ecuador. Hopefully, the latter will provide sufficient data to more thoroughly assess the conservation importance of Ayabaca province. In conclusion, Bosque de Cuyas is reconfirmed as an important site. That it persists so close to a major town is surprising, and every effort to protect it must be welcomed. Protecting the forest would not only secure populations of at least 14 distinctive range-restricted taxa, but also one of the largest ‘Tumbesian highland’ forests, a type that seems particularly in danger of disappearing. Acknowledgements Our study was an initiative of ProAves Pert with the additional participation of Abundio Segastegui (Universidad Nacional de Trujillo / Museo de Ciencias Naturales) and Angel Seminario (Municipalidad Provincial de Ayabaca). The study was funded by CARE International (Peru) and the Embassy of Finland in Lima. Logistical support was provided by the Mayor of Ayabaca, Manuel Otero Santur. Additional records were communicated by Paul Coopmans (Bosque de Cuyas), Jon Fjeldsa (Huamba) and Niels Krabbe (Utuana). Additional data on Atlapetes latinuchus from the Louisiana State Museum collection were provided by Dan Lane. Comments on earlier drafts by Jon Fjeldsa, Rob Williams, Thomas Schulenberg, Paul Coopmans and an anonymous reviewer are gratefully acknowledged. JNMF thanks Rob Williams, Mikko Pyhaéla and Nancy Hilgert for their company during field trips. References: Best, B. J., Clarke, C. T., Checker, M., Broom, A. L., Thewlis, R. M., McNab, A. & Duckworth, J. W. 1993. Distributional records, natural history notes and conservation of some poorly-known birds from south-west Ecuador and north-western Peru. Bull. Brit. Orn. Cl. 113: 108-120, 234-255. Best, B. J. & Kessler, M. 1995. Biodiversity and conservation in Tumbesian Ecuador and Peru. BirdLife International, Cambridge, UK. BirdLife International. 2000. Threatened birds of the world. BirdLife International, Cambridge, UK & Lynx Edicions, Barcelona. Bloch, H., Poulsen, M. K., Rahbek, C. & Rasmussen, J. F. 1991. A survey of the montane forest avifau- na of Loja province, southern Ecuador. International Council for Bird Preservation (Study Report No. 49), Cambridge, UK. Collar, N. J., Crosby, M. J. & Stattersfield, A. J. 1994. Birds to watch 2: the world list of threatened birds. BirdLife International (Conservation Series No. 4), Cambridge, UK. Fjeldsa, J. & Krabbe, N. 1990. Birds of the high Andes. Zool. Mus., Univ. of Copenhagen & Apollo Books, Svendborg. Flanagan, J. N. M., Vellinga, W. P. & Mark, T. R. 2000. Seven new locations for the Bearded Guan (Penelope barbata) from south-west Ecuador and north-west Peru. Bull. Cracid Specialist Group 11: 10-13. Willem-Pier Vellinga et al. 137 Bull. B.O.C. 2004 124(2) Franke, I. 1992. Biogeografia y ecologia de las aves de los bosques montanos del Pert occidental. Pp. 181—188 in Young, K. R. & Valencia, N. (eds.) Biogeografia, ecologia a y conservacion del bosque montano en el Peru. Mem. Hist. Nat. Univ. Nac. San Marcos. 21 Frimer, O. & Moller, S. 1989. The status of Polylepis forests and their avifauna in Cordillera Blanca. Zool. Mus., Univ. of Copenhagen. Garcia-Moreno, J. & Fjeldsa, J. 1999. Re-evaluation of species limits in the genus At/apetes based on mtDNA sequence data. /bis 141: 199-207. Garcia-Moreno, J., Ohlson, J. & Fjeldsa, J. 2001. MtDNA sequences support monophyly of Hemispingus tanagers, Mol. Phyl. & Evol. 21: 424-435. del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 1999. Handbook of the birds of the world, vol. 5. Lynx Edicions, Barcelona. Koepcke, M. 1961. Birds of the western slope of the Andes of Peru. Amer. Mus. Nov. 2028. Krabbe, N., Moore, J. V., Coopmans, P., Lysinger, M. & Ridgely, R. S. 2001. Birds of the Ecuadorian highlands—the upper montane and paramo zones of Ecuador. John V. Moore Nature Recordings, San Jose, CA. Parker, T. A., Schulenberg, T. S., Graves, G. R. & Braun, M. J. 1985. The avifauna of the Huancabamba region, northern Peru. Pp. 169-197 in Buckley, P. A., Foster, M. S., Morton, E. S., Ridgely, R. S. & Buckley, F. G. (eds.) Neotropical ornithology. Orn. Monogr. No. 36. Ridgely, R. S. & Greenfield, P. J. 2001. The The birds of Ecuador, vol. 1. Cornell Univ. Press, Ithaca, NY. Salinas, L., Franke, I., Samame, M. & Fjeldsa, J. 1998. Primer registro de Amaurospiza concolor (Emberizidae, Passeriformes) para el Peri. Libro de Resumenes, VII Reunion Cientifica, Inst. Invest. Ciencias Biol. “Antonio Raimondi’, Fac. Ciencias Biol., Univ. Nac. San Marcos 107. Salinas, L., Franke, I., Samame, M. & Fjeldsa, J. 2003. Primer registro del frutero pechinegro Pipreola lubomirskii (Aves, Cotingidae) en la vertiente occidental de los Andes. Rev. peru. biol. 10: 93-97. Schjellerup, I. (ed.) 2000. Yanchala—la gente y la biodiversidad. DIVA Tech. Publ. No. 10. Centro Bartolomé de las Casas, Lima & Danish Environ. Res. Inst., Copenhagen. Stattersfield, A. J., Crosby, M. J., Long, A. J., Wege, D. C. 1998. Endemic Bird Areas of the world: pri- orities for bird conservation. BirdLife International (Conservation Series No. 8), Cambridge, UK. Stotz, D. F., Fitzpatrick, J. F., Parker, T. A. & Moskovits, D. K. 1996. Neotropical birds: ecology and con- servation. Univ. Chicago Press. Wege, D. C. & Long, A. J. 1995. Key Areas for threatened birds in the Neotropics. BirdLife International (Conservation Series No. 5), Cambridge, UK. Weller, A.-A. 2000. Biogeography, geographic variation and habitat preference in the Amazilia Hummingbird, Amazilia amazilia Lesson (Aves, Trochilidae), with notes on the status of Amazilia alticola Gould, J Orn.141: 93-101. Whiffin, M. & Sadgrove, L. 2000. Expedicion Tumbes 2000—teporte preliminar. ProAves Peru, Piura. Williams, R. & Tobias, J. 1994. Final report of the Amaluza projects, 1990-1991. BirdLife International (Study Report No. 60), Cambridge, UK. Addresses: Willem-Pier Villenga, Groenesteinlaan 12, 9722 BZ, Groningen, The Netherlands, e-mail: vellinga@phys.rug.nl. Jeremy N. M. Flanagan, ProAves Peru, Av. José de Lama 1510, Sullana, Peru, e-mail: proaves@mail.udep.edu.pe. Todd R. Mark, 1880 White Oak Drive, Houston, TX, USA 77009, e-mail: moddtarks@hotmail.com Willem-Pier Vellinga et al. 138 Bull. B.O.C. 2004 124(2) APPENDIX 1 Species recorded at the Bosque de Cuyas, Aypate and E] Toldo, and at three similar nearby sites at comparable altitudes in Peru: Huamba (Schjellerup 2000), Cruz Blanca (Parker et al. 1985), and Ecuador: Utuana (N. Krabbe pers. comm.). Abbreviations used: ? = species doubtfully recorded; x? = species present, subspecies unclear; B = recorded only in Best et al. (1993); C = recorded only by P. Coopmans (pers. comm.); Y = around Yanchala. Figures indicate altitudes if species was recorded at a locality but outside the altitudinal range present in Bosque de Cuyas (2,000-3,000 m). ane Sune: se a 7 So & = Oe ae ae Z 208 BS au = Una 3 2 A §8 28 ~~ ° prtgets eS a = o aS) 2 ms ss ao S S) & N = Z eee Ee = nq < Be roe Nothoprocta pentlandii Andean Tinamou Xx Coragyps atratus Black Vulture x) ke ees x x Cathartes aura Turkey Vulture Kae eK x x Accipiter ventralis Plain-breasted Hawk X x X X x Buteogallus meridionalis Savannah Hawk Xx Geranoaetus melanoleucus Black-chested Buzzard-eagle 1 Xx X Buteo magnirostris Roadside Hawk X % x Buteo leucorrhous White-rumped Hawk X 1,750 Buteo albonotatus Zone-tailed Hawk x 1,750 Buteo brachyurus Short-tailed Hawk Z X Buteo polyosoma Red-backed Hawk Rta, ngXine lee Xx ms Buteo albigula White-throated Hawk Xx Harpyhaliaetus solitarius Solitary Eagle 3 Phalcoboenus megalopterus Mountain Caracara Sees x Penelope barbata Bearded Guan Xrwosey ux x % Columba fasciata Band-tailed Pigeon K vias | ae x Xx x Zenaida auriculata Eared Dove Kral Xt % Columbina cruziana Croaking Ground-dove ¥ Leptotila ochraceiventris Ochre-bellied Dove ? K Leptotila verreauxi White-tipped Dove Xx X x X Geotrygon frenata White-throated Quail-dove * x Xx xX Aratinga erythrogenys Red-masked Parakeet 2 ? Xx Aratinga wagleri Scarlet-fronted Parakeet 2 u x Bolborhynchus sp. Bolborhynchus sp. yi Forpus coelestis Pacific Parrotlet Y Amazona mercenaria Scaly-naped Parrot x Piaya cayana Squirrel Cuckoo X x ~ 1,850 Tapera naevia Striped Cuckoo X Crotophaga sulcirostris Groove-billed Ani x Cory 1,850 Tyto alba Barn Owl x Otus roboratus West Peruvian Screech-owl x Otus albogularis White-throated Screech-owl P x x Xx Willem-Pier Vellinga et al. Glaucidium jardinii Asio stygius Aegolius harrisii Lurocalis rufiventris Nyctidromus albicollis Caprimulgus longirostris Streptoprocne zonaris Cypseloides rutilus Aeronautes montivagus Colibri thalassinus Colibri coruscans Amazilia sp. Adelomyia melanogenys Aglaeactis cupripennis Lafresnaya lafresnayi Coeligena iris Ensifera ensifera Heliangelus micraster Heliangelus viola Lesbia nuna Lesbia victoriae Thaumastura cora Metallura tyrianthina Myrtis fannyi Acestrura mulsant Pharomachrus auriceps Trogon personatus Andigena hypoglauca Picumnus sclateri Veniliornis fumigatus Piculus rubiginosus Piculus rivolii Campephilus pollens Lepidocolaptes affinis Furnarius cinnamomeus Synallaxis azarae Hellmayrea gularis Cranioleuca antisiensis Margarornis squamiger Pseudocolaptes boissonneautii Syndactyla ruficollis Xiphocolaptes promeropirhynchus Lepidocolaptes lacrymiger Thamnophilus zarumae Myrmeciza griseiceps Grallaria squamigera Grallaria guatimalensis Grallaria ruficapilla Grallaria watkinsi Grallaria quitensis Grallaria rufula (cajamarcensis) 139 Andean Pygmy-owl Stygian Owl Buff-fronted Owl Rufous-bellied Nighthawk Pauraque Band-winged Nightjar White-collared Swift Chestnut-collared Swift Andean Swift Green Violetear Sparkling Violetear hummingbird sp. Speckled Hummingbird Shining Sunbeam Mountain Velvetbreast Rainbow Starfrontlet Sword-billed Hummingbird Little Sunangel Purple-throated Sunangel Green-tailed Trainbearer Black-tailed Trainbearer Peruvian Sheartail Tyrian Metaltail Purple-collared Woodstar White-bellied Woodstar Golden-headed Quetzal Masked Trogon Grey-breasted Mountain-toucan Ecuadorian Piculet Smoky-brown Woodpecker Golden-olive Woodpecker Crimson-mantled Woodpecker Powerful Woodpecker Spot-crowned Woodcreeper Pacific Hornero Azara's Spinetail White-browed Spinetail Line-cheeked Spinetail Pearled Treerunner Streaked Tuftedcheek Rufous-necked Foliage-gleaner Strong-billed Woodcreeper Montane Woodcreeper Chapman's Antshrike Grey-headed Antbird Undulated Antpitta Scaled Antpitta Chestnut-crowned Antpitta Watkins's Antpitta Tawny Antpitta Rufous Antpitta x ~ KK HK RK ~ KM mK ~~ MP ~ mM MM ~™ €-1 0) oo > mM ed Bull. B.O.C. 2004 124(2) x X x x v50 ? X X X X Xx X Xx x X X X Xx x X Xx X X x x X x Xx Xx X X X ss X X Xx Xx X X x x X Xx X Z x x x x % X x X x x x x X x X x x X Ds x Xx x x Xx x X i x % % ? x Xx % X x x X x X Zz x X X Xx x X X Xx x Sid 050+ x? Willem-Pier Vellinga et al. Grallaricula ferrugineipectus leymebambae Myornis senilis Scytalopus latrans subcinereus Phyllomyias nigrocapillus Phyllomyias uropygialis Zimmerius (chrysops) flavidifrons Elaenia obscura Elaenia albiceps Elaenia pallatangae Mecocerculus stictopterus Mecocerculus poecilocercus Mecocerculus leucophrys Mecocerculus calopterus Anairetes parulus Anairetes nigrocristatus Mionectes striaticollis Contopus fumigatus Poecilotriccus ruficeps Contopus cinereus Ochthoeca rufipectoralis Ochthoeca fumicolor Ochthoeca c. cinnamomeiventris Ochthoeca jelskii Myiotheretes striaticollis Myiotheretes fumigatus Attila torridus Myiarchus tuberculifer Myiodynastes chrysocephalus (minor) Tyrannus melancholicus Pachyramphus versicolor Pachyramphus albogriseus Ampelion rubrocristatus Pipreola arcuata Cyanolyca turcosa Cyclarhis gujanensis virenticeps Vireo leucophrys Catharus fuscater Catharus ustulatus Turdus fuscater Turdus serranus Turdus chiguanco Turdus reevei Mimus longicaudatus Progne chalybea Notiochelidon cyanoleuca Notiochelidon murina Campylorhynchus fasciatus Troglodytes musculus Troglodytes solstitialis 140 Rusty-breasted Antpitta Ash-coloured Tapaculo Blackish Tapaculo Black-capped Tyrannulet Tawny-rumped Tyrannulet Loja Tyrannulet Highland Elaenia White-crested Elaenia Sierran Elaenia White-banded Tyrannulet White-tailed Tyrannulet White-throated Tyrannulet Rufous-winged Tyrannulet Tufted Tit-tyrant Black-crested Tit-tyrant Streak-necked Flycatcher Smoke-coloured Pewee Rufous-crowned Tody-flycatcher Tropical Pewee Rufous-breasted Chat-tyrant Brown-backed Chat-tyrant Slaty-backed Chat-tyrant Jelski's Chat-tyrant Streak-throated Bush-tyrant Smoky Bush Tyrant Ochraceous Attila Dusky-capped Flycatcher Golden-crowned Flycatcher Tropical Kingbird Barred Becard Black-and-white Becard Red-crested Cotinga Barred Fruiteater Turquoise Jay Rufous-browed Peppershrike Brown-capped Vireo Slaty-backed Nightingale-thrush Spotted Nightingale-thrush Great Thrush Glossy-black Thrush Chiguanco Thrush Plumbeous-backed Thrush Long-tailed Mockingbird Grey-breasted Martin Blue-and-white Swallow Brown-bellied Swallow Fasciated Wren Southern House Wren Mountain Wren rm Ps Po a a oa x? a a as! rs PO Bull. B.O.C. 2004 124(2) x? mr OK a oo 2) rm oP a Willem-Pier Vellinga et al. Anthus bogotensis Parula pitiayumi Dendroica fusca Mvioborus miniatus Mvioborus melanocephalus Basileuterus nigrocristatus Basileuterus trifasciatus Basileuterus luteoviridis Basileuterus coronatus Euphonia cyanocephala Euphonia laniirostris Conirostrum cinereum Conirostrum sitticolor Conirostrum albifrons Diglossa caerulescens Diglossopis cyanea Diglossa humeralis Diglossa albilatera Diglossa sittoides Pipraeidea melanonota Tangara vassorii Tangara viridicollis Anisognathus lacrymosus Dubusia taeniata Thraupis episcopus Thraupis cyanocephala Piranga flava Thlypopsis ornata Hemispingus superciliaris Hemispingus verticalis Hemispingus (melanotis) piurae Saltator nigriceps Saltator cinctus Catamblyrhynchus diadema Pheucticus chrysogaster Sporophila luctuosa Amaurospiza concolor Catamenia inornata Sicalis flaveola Phrygilus plebejus ocularis Phrygilus alaudinus Haplospiza rustica Atlapetes leucopterus Atlapetes latinuchus (comptus) Atlapetes seebohmi Buarremon torquatus nigrifrons Zonotrichia capensis Dives warscewiczi Carduelis magellanica Carduelis psaltria 141 Paramo Pipit Tropical Parula Blackburnian Warbler Slate-throated Whitestart Spectacled Whitestart Black-crested Warbler Three-banded Warbler Citrine Warbler Russet-crowned Warbler Golden-rumped Euphonia Thick-billed Euphonia Cinereous Conebill Blue-backed Conebill Capped Conebill Bluish Flowerpiercer Masked Flowerpiercer Black Flowerpiercer White-sided Flowerpiercer Rusty Flowerpiercer Fawn-breasted Tanager Blue-and-black Tanager Silver-backed Tanager Lacrimose Mountain-tanager Buff-breasted Mountain-tanager Blue-grey Tanager Blue-capped Tanager Hepatic Tanager Rufous-chested Tanager Superciliaried Hemispingus Black-headed Hemispingus Piura Hemispingus Black-cowled Saltator Masked Saltator Plushcap Southern Yellow Grosbeak Black-and-white Seedeater Blue Seedeater Plain-coloured Seedeater Saffron Finch Ash-breasted Sierra-finch Band-tailed Sierra-finch Slaty Finch White-winged Brush-finch Rufous-naped Brush-finch Bay-crowned Brush-finch Stripe-headed Brush-finch Rufous-collared Sparrow Scrub Blackbird Hooded Siskin Lesser Goldfinch ~~ se mM x? x Ke MK MM Bull. B.O.C. 2004 124(2) xX x? x? 3,050+ X Xx x ~ OK Pe eo oe x KK MK ~ KM KM x Ms x eK Willem-Pier Vellinga et al. 142 Bull. B.O.C. 2004 124(2) APPENDIX 2 Comparison of some EBA 046 forests. Abbreviations: ? = species doubtfully recorded; x? = species present, subspecies unclear; VU = Vulnerable (BirdLife International 2000); NT = Near Threatened (BirdLife International 2000). Cruz Blanca (Parker ef al. 1985) Utuana (N. Krabbe pers. comm.) Huamba (Schyjellerup 2000) Amaluza (Williams & Tobias 1994) 5 ™ = s 3 io . = = < < za) Range-restricted taxa Penelope barbata VU x xX x x Coeligena iris x x x x Heliangelus viola X 5 Xx x x x Xe Heliangelus micraster x x Amazilia amazilia (alticola?) a Cranioleuca antisiensis x x xX is mS x & Myrmeciza griseiceps VU Xx X Syndactyla ruficollis VU x Xx x Leptotila ochraceiventris ? x Hemispingus piurae X x X Zimmerius (chrysops) flavidifrons x xe X x? Atlapetes seebohmi x x om Basileuterus trifasciatus x xX 26 me Thamnophilus zarumae By X x 26 Picumnus sclateri X Turdus reevei 2 x x Saltator nigrifrons x Ke x x xX Scytalopus latrans subcinereus X x x er x? xX x Aratinga erythrogenys 2 x Grallaria rufula cajamarcensis x Grallaricula ferrugineipectus x Ke xe Number of range-restricted taxa 14 14 13 7 12 8 5 Examples of easily recorded main-chain characteristic species Cyanocorax turcosa x X x x Anisognathus lacrymosus x X X x i Pipreola arcuata X x x a Cacicus holosericeus x Andigena hypoglauca x x x A. Townsend Peterson et al. 143 Bull. B.O.C. 2004 124(2) Detecting errors in biodiversity data based on collectors’ itineraries by A. Townsend Peterson, Adolfo G. Navarro-Sigtienza &© Ricardo Scachetti Pereira Received 24 April 2003 Museum curators have long checked the veracity of specimen data via collectors’ field notes, thus establishing whether a particular specimen could have been collected at the claimed place and/or date. In fact, at least one institution (Museum of Vertebrate Zoology, Berkeley, California) invests heavily in its archive of collec- tors’ field notes and has dedicated enormous effort to make this information increasingly useful (http://elib.cs.berkeley.edu/mvz/). This source of confirmatory tests of veracity of specimen data, however, would seem at first glance to be available only when detailed (and honest) field notes, journals and catalogues are available. The idea of checking itinerary information, however, can take on a new relevance with the development of large biodiversity datasets. The example upon which the analyses developed herein are based is that of the birds of Mexico, a databasing project that has covered the Mexican bird holdings of essentially all relevant natural history museums (Peterson ef al. 1998). This example, however, is increasingly relevant in general: as large biodiversity datasets are assembled from widely distributed sources, such detailed, multi-institutional information will become available for many taxa and regions (e.g., Species Analyst, http://speciesan- alyst.net; Red Mundial de la Informacidn de la _ Biodiversidad http://www.conabio.gob.mx). The purpose of this contribution is thus, to develop the framework of a method- ology for identifying potential errors in geo-referencing or in the date of collection of specimens by particular collectors. The general approach is that of assembling all of the specimens collected from a particular collector in temporal order, and imposing criteria of maximum radii of likely movement within a day, or over small numbers of days. Although preliminary, and requiring customisation for particular applications, the approach is developed and tested on five Mexican bird collectors. Methods Data from 33 core natural history museums in North America and Europe were used in the development of this example. This dataset (c.400,000 records) (Peterson et al. 1998) was queried for all specimens of each collector, and the top four collec- tors in terms of productivity were chosen for analysis (Chester C. Lamb, collecting 1920-1969, 41,184 specimens; Wilmot W. Brown, collecting 1890-1953, 18,238 specimens; Mario del Toro Aviles, collecting 1926-1958, 8,744 specimens; A. R. A. Townsend Peterson et al. 144 Bull. B.O.C. 2004 124(2) Phillips, collecting 1923-1989, 7,148 specimens). All of these collectors are now deceased and all were sufficiently productive (Fig. 1) in terms of number of specimens to provide adequate samples for analysis. We also included the 1,458 specimens collected by one of us (AGNS) as an example of specimens for which data were assembled with great care. Specimen collection localities were assigned geographic coordinates based on visual inspection of 1:50,000 topographic maps; specimens for which precise geo-referencing was not possible were excluded from analyses. Records were filtered to keep only those for which both dates and geo- references were available, leaving 40,114 (Lamb), 17,809 (Brown), 7,051 (del Toro Aviles), 6,887 (Phillips) and 1,456 (AGNS) (Fig. 1). Records of each collector were assembled in Microsoft Excel worksheets and sorted in order of date, and within dates by longitude and then latitude (ideally, localities should have been sorted by geographic proximity, but this was not done for computational simplicity). Distances (km) between one locality (latl, long1) and the next (lat2, long2) were calculated from the spherical trigonometry formula: SIN iad 1/57. 2958 ) SIN (lat 2 (57. 2958)+ — Distance = 6378" ACOS| COS Gaz 1157 2958) COS reese COS (long 2/ 57.2958) (long1/57.2958)) (drawn from http://www.auslig.gov.au/geodesy/datums/distance.htm). Criteria for identifying potential errors were chosen using a set of assumptions regarding the ability of collectors to move particular distances within particular time intervals. For purposes of demonstration, we used 40 km moved in a single day, 100 km moved from one day to the next, 200 km moved in two days, and 500 km moved in three days as a set of assumptions. These criteria were chosen arbitrar- ily to represent distances greater than the maximum distances that collectors typically move in particular time intervals. Clearly, if this methodology were to be implemented more broadly, these assumptions could be varied to match particular collectors: collectors moving on horseback could be assigned shorter distance criteria than collectors moving by automobile on more modern roads. Crude potential errors were summarised as number per 1,000 specimens for which a potential problem was detected (i.e., number of potential errors identified per number of specimens collected on the same day as another specimen, on the day after another specimen, etc.). For a subset of records (Phillips’ specimens only), records identified as potential problems were categorised, by laborious visual inspection, into those situations that were most likely to be correct (e.g., collector collected one specimen in one site, and then moved 62 km to another site, and collected more specimens), versus those that were more likely to be erroneous, and into an estimate of actual number of possible errors (e.g., if two sites 1,000 km apart A. Townsend Peterson et al. 145 Bull. B.O.C. 2004 124(2) TABLE | AGNS Brown Lamb Phillips del Toro Aviles Days No. No. No. No. No. No. No. No. No. No. specimens potential specimens potential specimens potential specimens potential specimens potential analysed errors analysed errors analysed errors analysed errors analysed errors 0 1,220 2 13:55) 209 = 34,346 730 4,586 480 5,079 18] l 154 2 2,365 113 4,339 553 1,147 385 1,316 160 2 ll | 774 23 464 101 305 100 186 15 3 l 0 321 5 165 35 45 23 71 2 Q-error 0.0016 0.0154 0.0213 0.1047 0.0357 l-error 0.0130 0.0478 0.1274 0.3357 0.1216 2-error 0.0909 0.0297 0.2177 0.3279 0.0807 3-error 0 0.0156 0.2121 0.5111 0.0282 were reported as being sampled during seven consecutive days, one error occurred, rather than seven). Results The five collectors analysed herein present diverse results in terms of error detection and analysis. Specimens collected by AGNS, as a first example, held a total of five potential errors out of 1,456 specimens (Table 1). Of these specimens with potential errors, four were somewhat long-distance moves in relatively short amounts of time: for instance, after collecting for several days in the Sierra de Juarez, Oaxaca, in early November 1987, AGNS moved 127 km between 5 and 6 November, and collected one bird at La Tinaja, Veracruz (Black Vulture Coragyps atratus, MZFC 6395). Checking field notes for this collection indicated that this specimen was a road-kill, and was indeed collected where and when its data indicated; such was the case for one other specimen. Three specimens, however, indeed held errors of geo-referencing (Fig. 1). For example, based on his specimen label data, AGNS moved 541 km between collecting events on 19 and 20 April 1992. Inspection of his field notes indicated that he collected at Chiquihuites, Volcan Tacana, Chiapas, on 16-19 April, and at Papales, Volcan Tacana, Chiapas, on 20-21 April. These two localities are not 450 km apart; rather, the geographic reference for Papales proved to represent an error of 5° of longitude. In fact, the two localities are only a few km apart, signifying true errors (post-collection) in data records associated with specimens collected by AGNS. The other four collectors—in reality the object of this study—showed higher apparent error rates (Table 1). Error rates, calculated under the different distance- time criteria, for Brown ranged 0.015—0.050 per thousand, those for del Toro Aviles 0.028—0.122, for Lamb 0.021—0.218, and for Phillips 0.105—0.511 (see Table 1). Specimens indicated as potentially erroneous revealed many clear cases of error; for example, Phillips’ collections in early October 1955 were focused in Sinaloa and Nayarit (Fig. 1), including collections on 8 October 1955. However, also on 8 A. Townsend Peterson et al. 146 Bull. B.O.C. 2004 124(2) October 1955, a specimen of Rufous- capped Warbler Basileuterus rufifrons (DMNH 26575) was apparently from Acahuizotla, Guerrero, and clearly represents an impossible jump (c.700 km) for a single collector (Fig. 2). Each of the four collectors showed several such clear examples of error; a rough estimate of numbers of actual errors (e.g., two distant localities on the same date, etc., omitting cases in which travel by automobile would have made such distances possible) for Phillips was about 65 probable errors. Discussion The approaches explored herein are not new: curators and collection managers of natural history museums have long used collectors’ itineraries to assess the veracity of specimen data. What is new is the implementation of these approaches in an exploratory sense, seeking to identify specimens that have high probabilities of error without prior reason to suspect problems. Beyond simple error detection, these methods offer an opportunity to begin to understand objectively the ways in which scientific collections were assembled. In this case, errors of geo-referencing or dating are identified; additional approaches focusing on other sources of error have also been identified, and error-detection tools developed (Chapman 1999). An Figure 1. Maps of collecting localities for each of the five collectors analysed in this paper: (A) AGNS, (B) Brown, (C) Lamb, (D) del Toro Aviles, and (E) Phillips. The geo-referencing error detected in AGNS’s specimen data is evident off the coast of Guerrero. Collecting localities are roughly classed as to year of collection by five shades from black (oldest specimens) to white (newest specimens). A. Townsend Peterson et al. 147 Bull. B.O.C. 2004 124(2) important point, however, is that these methodologies are not being developed with the aim of designating particular collectors as ‘good’ or ‘bad’, but rather as a way of identifying potential problems among the data records from each collector. Limitations The methods explored herein can fail under three circumstances. First, the temporal density of records from a particular collector must be sufficient to permit detection of potential problems. For low-volume collectors, the probability that erroneous records would overlap sufficiently in time to allow detection of problems would be relatively low, so these methods will frequently miss problems with such collectors. A second limitation is for situations in which specimens are listed as stemming from a single collector, but more than one collector was really involved. Examples, such as Adolphe Boucard across much of the world, are well known as listing the efforts of multiple collectors under a single name. Three of the collectors analysed herein (Brown, Lamb, del Toro Avilés) had no such arrangements. Lamb and often Phillips apparently worked with teams of collectors, although to our knowledge these teams usually remained together in groups (A. R. Phillips pers. comm. to ATP, December 1988); one possible explanation for the complications among Phillips’ specimens, however, is that some of Phillips’ specimens may have been acquired Figure 2. Map of collecting localities for Allan R. Phillips for 2-10 October 1955, showing a locality in Guerrero on 8 October 1955 that is probably erroneous. A. Townsend Peterson et al. 148 Bull. B.O.C. 2004 124(2) from his collectors, who may have continued accumulating specimens (and labelled them under his name) when not in the field with Phillips. More general application of these methods must nevertheless bear in mind that such collectors who included catalogue entries from multiple collectors and preparators will often produce false indications of errors. The final, and darkest, possibility is that of complete fabrication of data. That is, if a malicious collector simply invented everything, in this way, it would be possible to make the associated information completely consistent. This complete fabrication, rather than errors or fabrications associated with single specimens, would not be detected by the approaches developed herein. Causes of errors detected A diversity of factors can produce the types of errors that have been detected in this study. They range from mistakes in data recording to deliberate falsification and, of course, have very different implications as a result. Going beyond simply detecting errors then becomes important: analysis of the types and causes of errors detected permits learning about the methods and motives of each collector, and may allow detection of additional errors that could have important implications for biodiver- sity inventories. Errors can be divided into two general types: collector errors and post-collec- tion errors. Post-collection errors can enter the process at a variety of points. In older collections, such as with the Salvin and Godman collections from Mexico and Central America, specimen labels were at times prepared at the museum well after the collector’s involvement (Godman 1915), creating considerable opportunity for mistakes. An excellent example of this effect_is for the type specimen of the woodnymph Thalurania luciae (Deignan 1961), which is labelled as collected in the Tres Marias Islands off western Mexico, and described as a species new to science; in reality, it was from Brazil, its data having probably been confused between two collections arriving at the U.S. National Museum of Natural History at the same time. Numerous subsequent phases, including re-labelling, cataloguing, computer- isation, and geo-referencing, provide additional opportunities for errors to come into existence. Collector errors are perhaps more complex. Certainly, some of these problems are simple mistakes: a collector noted an incorrect date or locality on the label. Brown, according to Phillips (pers. comm. to ATP, December 1988), had an amusing source of error: labels with locality information were apparently made up prior to collection and placed in the skinning kit. If all of the pre-made labels were not used at a particular site, however, the remainder apparently stayed in the skinning kit, and would be used (accidentally) at succeeding localities. This sort of error would produce a clear signature of past, well-sampled localities appearing as scattered errors at later sites. Such a signature is indeed present in at least some Brown collections: for instance, a specimen of Olive Sparrow Arremonops [rufivir- gatus| sumichrasti (MCZ 164687) was supposedly collected on 31 January 1931 at A. Townsend Peterson et al. 149 Bull. B.O.C. 2004 124(2) Acapulco, Guerrero, when the collector was collecting numerous specimens from Coyuca, Guerrero (e.g.. MCZ 163991). Acapulco, however, was sampled intensively on 9 December 1930-8 January 1931 (e.g.. MCZ 163887). Nevertheless, overall, Brown’s specimens appear to be relatively clean, without overwhelming numbers of errors produced by his apparent carelessness regarding labels. A still-worse source of error is that in which labels were not prepared at the time of collection. The famous example here is that of Mario del Toro Aviles, who apparently had more than 10,000 unlabelled specimens in his house when visited by A. R. Phillips (Binford 1989). This utter lack of interest in accuracy of label information has caused numerous problems, including many odd locality and date records (Binford 1989), and even species for which the type locality is most likely inaccurate (Peterson & Nieto-Montes de Oca 1996). This pattern of collector behaviour produces the relatively numerous random locality and date records that characterise del Toro Aviles’ specimens, although del Toro Aviles ranked well behind Lamb and Phillips in terms of error rates detected. The higher error rates detected among the specimens of Lamb and Phillips are quite surprising. In both cases, the collector had been considered to be relatively reliable and no previous commentary had addressed potential problems with their material. This implication of potential problems thus demands a more in-depth, biographical analysis of these collectors. Most difficult to manage are errors that involve deliberate falsification of data. The most famous such doings are those of the collector Richard Meinertzhagen, who apparently stole specimens, re-labelled them, and sometimes even re-prepared them to give the appearance that he had collected them himself (Knox 1993, Rasmussen & Collar 1999). As mentioned above, such broad falsification would be difficult to detect using the methodologies developed herein. Nevertheless, errors among the specimens of Allan R. Phillips are suspicious— certainly, potential error rates associated with his specimens are higher than would have been expected, so we must consider additional information regarding Phillips’ work as a collector. First, error rates among his specimens are high, indeed many times those of Mario del Toro Aviles, whom Phillips criticised so thoroughly (A. R. Phillips pers. comm. to ATP, December 1988). Second, Phillips was very concerned about specimen data, e.g., in respect of moult patterns, migration records and subspecific variation, so it seems unlikely that he would make so many random errors. Third, comments made by Phillips (pers. comm. to ATP, December 1988) regarding collecting specimens indicated that when he collected specimens during periods for which he had no collecting permits, he would change dates to those time periods for which permits were available. Finally, during museum studies as part of the assembly of the Atlas, several specimens were encountered by AGNS in Phillips’ personal collection that were collected by students and staff at Universidad Nacional Autonoma de México and other Mexican institutions, including specimens collected by AGNS himself! The implications of such findings beg A. Townsend Peterson et al. 150 Bull. B.O.C. 2004 124(2) further information, perhaps from Phillips’ colleagues and associates, which would illuminate the situation further and might permit a decision as to whether major portions of Phillips’ material should be ignored in considerations of the specimen record of Mexican birds. Implementation Clearly, a central concern for any broad implementation of these methodologies should be the suites of assumptions regarding the ability of different collectors to move particular distances per unit time. We have, in this prototype of the method, used a ‘middle-of-the-road’ suite of assumptions, solely for the purposes of demonstration. Clearly, modern collectors (e.g., AGNS) could be treated differently from the former collectors (e.g., Brown), which would result in greater precision in error detection. In this sense, consideration of some biographical information regarding each collector could greatly enrich our error-detection approaches. Tools for broad implementation of these error-detection approaches are presently under development. A first requirement is that of large quantities of biodiversity information, in which collectors’ entire specimen collections are assembled. Such assemblies of information necessarily depend on integrating information from across many institutions, as most collectors’ specimens are spread widely among them. Projects such as that of the Atlas of Mexican bird distributions, from which the present dataset is drawn, require intense investment in data manage- ment and for that reason there are at present few such projects (Peterson et al. 1998, Navarro-Siguenza et al. 2002). An alternative approach is that of distributed biodiversity databases, which integrate electronic databases housed at different institutions via the Internet. Nevertheless, a considerable time lag is involved in the creation of such electronic databases, particularly for methods such as this one that require complete information for full functionality. Acknowledgements We thank the curators and staff of the following scientific collections for access to specimens and data under their care: American Museum of Natural History; Academy of Natural Sciences of Philadelphia; Bell Museum of Natural History; British Museum (Natural History); California Academy of Sciences; Carnegie Museum of Natural History; Canadian Museum of Nature; Denver Museum of Natural History; Delaware Museum of Natural History; Fort Hays State College; Field Museum of Natural History; Iowa State University; University of Kansas; Los Angeles County Museum of Natural History; Natuurhistorische Museum; Louisiana State University Museum of Zoology; Museum of Comparative Zoology, Harvard University; Moore Laboratory of Zoology, Occidental College; Muséum Nationale d’Histoire Naturelle; Museum of Vertebrate Zoology, Berkeley; Museo de Zoologia, Facultad de Ciencias, Universidad Nacional Autonoma de México; University of Nebraska; Royal Ontario Museum; San Diego Natural History Museum; Southwestern College; Texas Cooperative Wildlife Collections; University of Arizona; University of British Columbia Museum of Zoology; University of California Los Angeles; Universidad Michoacana de San Nicolas de Hidalgo; United States National Museum of Natural History; Western Foundation of Vertebrate Zoology; and Peabody Museum, Yale University. This study was supported by the U.S. National Science Foundation. ATP’s work (in Brazil) was supported by a grant from the Fundagao de Amparo 4 Pesquisa do Estado de Sao Paulo. A. Townsend Peterson et al. 151 Bull. B.O.C. 2004 124(2) References: Binford, L. C. 1989. A distributional survey of the birds of the Mexican state of Oaxaca. Orn. Monogr. No. 43. Chapman, A. D. 1999. Quality control and validation of point-sourced environmental resource data. Pp. 409-418 in Lowell, K. (ed.) Spatial accuracy assessment: land information uncertainty in natural resources. Ann Arbor Press, Chelsea, MI. Deignan, H. G. 1961. Type specimens of birds in the United States National Museum. Smithsonian Inst. Bull. 1961: 1-718. Godman, F. D. 1915. Biologia Centrali Americana: introductory volume. Taylor & Francis, Ltd., London. Knox, A. G. 1993. Richard Meinertzhagen—a case of fraud examined. /bis 135: 320-325. Navarro-Sigtienza, A. G., Peterson, A.T. & Gordillo-Martinez, A. 2002. A Mexican case study on a cen- tralized database from world natural history museums. CODATA Journal 1: 45-53. Peterson, A. T., Navarro-Sigtienza, A. G. & Benitez-Diaz, H. 1998. The need for continued scientific col- lecting: a geographic analysis of Mexican bird specimens. /bis 140: 288-294. Peterson, A. T. & Nieto-Montes de Oca, A. 1996. Sympatry in Abronia (Squamata: Anguidae) and the problem of Mario del Toro Aviles’ specimens. J. Herpetology 30: 260-262. Rasmussen, P. C. & Collar, N. J. 1999. Major specimen fraud in the forest owlet Heteroglaux (Athene auct.) blewitti. Ibis 141: 11-21. Rasmussen, P. C. & Prys-Jones, R. P. 2003. History vs mystery: the reliability of museum specimen data. Bull. Brit. Orn. Cl. 123A: 66-94. Addresses: A. Townsend Peterson, Natural History Museum and Biodiversity Research Center, The University of Kansas, Lawrence, Kansas 66045, e-mail: town@ku.edu. Adolfo G. Navarro- Sigiienza, Museo de Zoologia, Facultad de Ciencias, Universidad Nacional Autonoma de México, Apartado Postal 70-399, Mexico, D.F. 04510, Mexico. Ricardo Scachetti Pereira, Centro de Referéncia em Informacao Ambiental, Av. Romeu Tortima 388, Barao Geraldo 13084-520 Campinas S.P., Brazil. © British Ornithologists’ Club 2004 Rediscovery of the White-necked Picathartes Picathartes gymnocephalus in Ghana by Ben D. Marks, Fason D. Weckstein, Kevin P Fohnson, Mathys 7. Meyer, James Braimah & Fames Oppong Received 1 Fuly 2003 The White-necked Picathartes Picathartes gymnocephalus is endemic to the Upper Guinean forests of West Africa (Fry et al. 2000) from Guinea to Ghana. Throughout this range, the rapid fragmentation and destruction of lowland rain forest threatens the survival of this remarkable species (BirdLife International 2000). Recent studies have focused on various demographic and ecological questions regarding popula- tions of P gymnocephalus in Guinea (Halleux 1994), Liberia (Allport 1991), Sierra Leone (Thompson 1993, 2001, Thompson & Fotso 2000), and Ivory Coast (Salewski et al. 2000). However, no recent records of this bird are available from Ghana. The most recent published records of Picathartes in the country are those of Ben D. Marks et al. 152 Bull. B.O.C. 2004 124(2) Grimes (1964, Grimes & Darku 1968), the latter summarising results from a 1966 survey. Since the 1960s, attempts to locate this species in Ghana have been unsuccessful (John Mason pers. comm.). As a result, it was widely believed that P gymnocephalus had been extirpated from Ghanaian forests. Here we report on the recent rediscovery of P gymnocephalus in the Brong-Ahafo Region, Ghana. On 14-30 March 2003 we conducted an avifaunal survey in a block of forest reserves in Brong-Ahafo Region. Our survey relied heavily on a line of 26 consec- utively-strung mist-nets running along the boundary line between Ayum and Subim forest reserves (06°71’N, 02°73’W). The forest in this region is dominated by Celtis spp., Ceiba and Pterogota tree species and has many large boulders and rocky outcrops. On 26 March 2003 at 1040 h we mist-netted a P gymnocephalus (Fig. 1), videotaped, photographed and released it unharmed. On 28 March 2003 we showed the video of the Picathartes to a local hunter in Asumura to discover whether he was familiar with the species. He immediately recognised the bird and told us that he had encountered at least three individuals in the nearby forest reserves. He reported some of the life history attributes of the species, such as breeding period (the fifth month of the year) and nest site. On 30 March he led us to a nest site. The nests were located on a boulder c.5 m high with a cave-like overhanging face sloping at a steep angle down to the ground. The two nests were constructed from mud and plant fibres, attached to the overhang with the cup of the nest forming a semi-circle c.30 cm wide, 15 cm high, and 15 cm deep. They were positioned less than 1 m apart at approximately the same height (c.2.5 m). On the floor of the shelter formed by the SE Figure 1. Picathartes gynmochepalus mist-netted in Ghana on 26 March 2003 (J. D. Weckstein & B. D. Marks) Ben D. Marks et al. 153 Bull. B.O.C. 2004 124(2) over-hanging rock were several hundred snail shells; snails are a potential food source for this species (Fry et a/. 2000). The local hunter noted that when he first found this nesting site there was only one nest and that the second nest was new. JO and the hunter revisited the nesting site on 22 April 2003 and noted that one of the nests had undergone further construction, making it 18.5 cm high. The activity at the nest site, coupled with the hunter’s report of other Picathartes in different sites in this forest reserve system, suggest that this location may hold a viable population of Picathartes. The Ghana Wildlife Division, Nature Conservation Research Centre (NCRC, a Ghanaian NGO), and the Chief of Asumura are making an effort to protect the species in these reserves. Further work is needed to census the area for other individuals and nests to determine the viability of this Picathartes population. Acknowledgements We thank the Ghana Wildlife Department for their continued support of our research programme in Ghana. In particular we would like to thank Mike Adu-Nsiah for all of his help with permits and his enthusiasm for our work. John Mason, Patrick Adjewodah and Mavis Boateng from NCRC, as well as Samuel Agyei, provided invaluable logistical support during all phases of this project. We also thank Frank Agbeko, the people of Asumura, and especially Nana Prince Yaw Adomako for granting us access to the forest reserves. Finally we thank the Louisiana State Museum of Natural Science and NSF PEET DEB-0118794 to KPJ for financial support. References: Allport, G. (1991) The status and conservation of threatened birds in the Upper Guinea forest. Bird Conserv. Intern. 1: 53-74. BirdLife International. 2000. Threatened birds of the world. BirdLife International, Cambridge, UK & Lynx Edicions, Barcelona. Fry, C. H., Keith, S. & Urban, E. K. (eds.) 2000. The birds of Africa, vol. 6. Academic Press, London. Grimes, L. 1964. Some notes on the breeding of Picathartes gymnocephalus in Ghana. [bis 106: 258-260. Grimes, L. & Darku, K. 1968. Some recent breeding records of Picathartes gymnocephalus in Ghana and notes on its distribution in West Africa. bis 110: 93-99. Halleux, D. 1994. Annotated bird list of Macenta Prefecture, Guinea. Malimbus 16: 10-29. Salewski, V., Goken, F., Korb, J. & Schmidt, S. 2000. Has the White-necked Picathartes Picathartes gym- nocephala still a chance in Lamto, Ivory Coast? Bird Conserv. Intern 10: 41-46. Thompson, H. S. 1993. Status of White-necked Picathartes—another reason for the conservation of the Peninsula Forest, Sierra Leone. Oryx 27: 155-158. Thompson, H. S. 2001. Body mass, measurements and moult of the White-necked Picathartes, Picathartes gymnocephalus, in Sierra Leone. Ostrich 72: 209-212. Thompson, H. S. & Fotso, R. 2000. Conservation of two threatened species: Picathartes. Ostrich 71: 154-156. Addresses: Ben D. Marks & Jason D. Weckstein, Department of Biological Sciences and Museum of Natural Science, 119 Foster Hall, Louisiana State University, Baton Rouge, LA 70808, USA, e-mail: bmarksS@Isu.edu. Kevin P. Johnson & Mathys J. Meyer, Illinois Natural History Survey, 607 East Peabody Drive, Champaign, IL 6182, USA. James Braimah & James Oppong, Ghana Wildlife Division, Forestry Commision, P.O. Box M.239, Accra, Ghana. © British Ornithologists’ Club 2004 Harold F- Greeney 154 Bull. B.O.C. 2004 124(2) A nest of the Spot-fronted Swift Cypseloides cherriei in eastern Ecuador by Harold F Greeney Received 20 Fuly 2003 Among the most poorly known species in South America is the Spot-fronted Swift Cypseloides cherriei. Originally described from Costa Rica 110 years ago (Ridgway 1893), it was considered to be confined to a single locality there for over 50 years (Peters 1940) until specimens were reported from Colombia and Venezuela (Zimmer 1945, Beebe 1949). Whilst its range is now known to extend to both slopes of the Andes in northern Ecuador (del Hoyo et al. 1999, Ridgley & Greenfield 2001), its distribution is disjunct and poorly understood. Little has been reported concerning the behaviour of Spot-fronted Swift in Ecuador (but see Moore et al. 1999, Ridgely & Greenfield 2001, Howell 2002), and the only reports of breeding activity are from Rancho Grande in Venezuela (Collins 1980) and central Costa Rica (Marin & Stiles 1992). Here I present observations of Spot-fronted Swift in north-east Ecuador. Observations were made at Cabanas San Isidro preserve, in Napo province, c.3 km west of Cosanga and adjacent to the Yanayacu Biological Station & Center for Creative Studies (00°35’S, 77°53’W). The preserve encompasses primary and disturbed forest at 2,000—2,500 m in elevation and experiences a wetter season from roughly February to July. Whilst bird watchers and ornithologists have appreciated the uniqueness of this area for nearly 20 years, little has been published about the site and ornithological studies have only recently drawn more attention to its avifauna (Greeney 2002, Dobbs et al. 2003, Price 2003, Greeney ef al. 2004). On 27 May 2002 at 1300 h an adult Spot-fronted Swift was found sitting in a seemingly completed but empty nest in the relatively level area of primary forest west of the Cosanga River at 2,050 m. The nest was within a small cave created by a pile of large boulders through which a small stream was running. Overall, the cave was c.3 m high at the highest point and accessible from three entrances, each c.1.5 m high and 1.5—2.5 m wide. The nest had been constructed on top of an old Chestnut-collared Swift Cypseloides rutilus nest that had successfully fledged two young the previous October (Greeney unpubl. data). It was 1.5 m above the stream, 35 cm from the top of the cave at this point, and located on an outward-curving rock face. It was slightly smaller than the remnants of the Chestnut-collared Swift nest, which created a platform to support the new nest. The nest was a shallow cup formed entirely of fresh green mosses, lichens, liverworts and pieces of ferns. Unfortunately the nest was found destroyed two weeks later and no further observa- tions were possible. Harold F. Greeney 155 Bull. B.O.C. 2004 124(2) The cave where this nest was found has been used for breeding over the past four years by Chestnut-collared Swifts (Greeney unpubl. data). This species breeds in August—January in the area, roughly corresponding to the drier months. This, and other similar nesting sites of the Chestnut-collared Swift are used as roosting sites throughout the year. The exact nest site of the Spot-fronted Swift was re-used in September—December 2002 and 2003 by a pair of Chestnut-collared Swifts. It is unknown whether Chestnut-collared Swifts were using this cave as a roost in May 2002, but no other active nests were found. Collins (1980) noted the proximity of Spot-fronted Swift nests to those of Chestnut-collared Swift nests in Venezuela. Breeding activity for both species was recorded in the wet season in that area (Beebe & Crane 1947, Collins 1980). Chestnut-collared Swifts breed during the dry season in this area of north-east Ecuador (Greeney unpubl. data), whereas all previous studies have indicated the species to breed in the wet season (Snow 1962, Collins 1968, Marin & Stiles 1992). The nest of Spot-fronted Swift observed here was during the wet season. Work on swiftlets (Collocalia) in Indonesia suggested that species sharing roost sites used foraging times as a resource-partitioning mechanism (Medway 1962, Harrison 1974). Whilst both of the Cypseloides swifts discussed here are often seen foraging together in Ecuador (Howell 2002, M. Lysinger pers. comm.), and Collins (1980) suggested a similar resource-partitioning hypothesis for observations in Venezuela (Beebe 1949, Schafer & Phelps 1954), the information presented here suggests a different ecological relationship between these congenerics in our area. My observations warrant further investigation of possible niche partitioning for these species in north-east Ecuador and point to the need for basic natural history and observational studies on these and many other Neotropical birds. Acknowledgements I am deeply indebted to Carmen Bustamante and Mitch Lysinger at Cabafias San Isidro, for their patience, support, and guidance. C. T. Collins and R. C. Dobbs generously provided comments and litera- ture. Ruth Ann & John V. Moore generously provided funds to encourage my natural history observations and the PBNHS continues to provide support and assistance. This is publication number 27 of the Yanayacu Natural History Research Group. References: Beebe, W. 1949. The swifts of Rancho Grande, north-central Venezuela with special reference to migra- tion. Zoologica 34: 53-62. Beebe, W. & Crane, J. 1947. Ecology of Rancho Grande, a subtropical cloud forest in northern Venezuela. Zoologica 32: 43-66. Collins, C. T. 1968. The comparative biology of two species of swifts in Trinidad, West Indies. Bull. Florida State Mus. 11: 257-320. Collins, C. T. 1980. The biology of the Spot-fronted Swift in Venezuela. Amer. Birds 34: 852-855. Dobbs, R. C., Greeney, H. F. & Martin, P. R. 2003. The nest, nesting behavior, and foraging ecology of the Rusty-winged Barbtail (Premnornis guttuligera). Wilson Bull. 115: 367-373. Harold F Greeney 156 Bull. B.O.C. 2004 124(2) Greeney, H. F. 2002. First description of the nest for the Bicolored Antvireo (Dysithamnus occidentalis), with notes on its behavior in eastern Ecuador. Orn. Neotrop. 13: 297-299. Greeney, H. F, Hannelly, E. C. & Lysinger, M. 2004. First description of the nest and vocalisations of the Peruvian Antpitta Grallaricula peruviana with a northward range extension. Cotinga 21: 14-17. Harrison, T. 1974. The food of Collocalia swiftlets (Aves, Apodidae) at Niah Great Cave in Borneo. J. Bombay Nat. His. Soc. 71: 376-393. Howell, S. N. G. 2002. Additional information on the birds of Ecuador. Cotinga 18: 62-65. del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 1999. Handbook of the birds of the world, vol. 5. Lynx Edicions, Barcelona. Marin A., M. & Stiles, F G. 1992. On the biology of five species of swifts (Apodidae, Cypseloidinae) in Costa Rica. Proc. West. Found. Vert. Zool. 4: 286-357. Medway, Lord. 1962. The swiftlets (Collocalia) of Niah Cave, Sarawak. Ibis 104: 228-245. Moore, J. V., Coopmans, P., Ridgely, R. S. & Lysinger, M. (1999) The birds of northwest Ecuador, 1. J. V. Moore Nature Recordings, San Jose, CA. Peters, J. L. 1940. Check-list of birds of the world, vol. 4. Harvard Univ. Press, Cambridge, MA. Price, E. R. 2003. First description of the nest, eggs, hatchlings, and incubation behavior of the White- bellied Antpitta (Grallaria hypoleuca). Orn. Neotrop. 14: 535-539. Ridgway, R. 1893. Descriptions of two supposed new species of swifts. Proc. U.S. Natl. Mus. 16: 43-44. Ridgely, R. S. & Greenfield, P. J. 2001. The birds of Ecuador. Cornell Univ. Press, Ithaca, NY. Schafer, E. & Phelps, W. H. 1954. Las aves del parque nacional “Henri Pittier” (Rancho Grande) y sus funciones ecologicas. Bol. Soc. Ven. Cienc. Nat. 83: 1-167. Snow, D. W. 1962. Notes on the biology of Trinidad swifts. Zoologica 47: 129-139. Zimmer, J. T. 1945. A new swift from Central and South America. Auk 62: 586-592. Addresses: Yanayacu Biological Station & Center for Creative Studies, Cosanga, Napo, Ecuador, c/o 721 Foch y Amazonas, Quito, Ecuador, e-mail: revymmoss@yahoo.com © British Ornithologists’ Club 2004 MEMBERSHIP See also website: http://www.boc-online.org Subscription rates for 2004 are again unchanged, and were due for renewal on | January 2004: BOU Members £12.00 US$ 24.00 Non-BOU Members £18.00 US$ 34.00 All paid-up Members of the Club receive (postage free) four quarterly issues of the Bulletin, and the annual index. New Members are welcomed, at any time. CORRESPONDENCE Correspondence on all general Club matters should be addressed to: The Hon. Secretary, S.A.H. (Tony) Statham, Woodcock Hill, Durrants Lane, Berkhamsted, Herts. HP4 3TR UK (or e-mail: SAHS@tinyonline.co.uk). For details of Club Meetings see inside front cover. Correspondence and applications for membership, and changes of address should be addressed to: The Membership Secretary, Cdr. M.B. 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Publications Officer BOC, Natural Resources Institute, University of Greenwich at Medway, Central Avenue, Chatham Maritime, Chatham, Kent ME4 4TB (e-mail: r.a.cheke@greenwich.ac.uk) PAYMENTS All amounts quoted are net and should be paid in £ sterling, if possible. Payments in other currencies must include a further £4 for UK bank charges (except for annual rates in US dollars, which are inclusive). All cheques or drafts should be made payable to the British Ornithologists’ Club. If preferred, remittances may be made by bank transfer direct to the Club’s bank account: Barclays Prime Account, Dale House, Wavertree Boulevard, Liverpool L7 9PQ, UK (Sort Code 20-00-87, Account No. 10211540), with confirmation to the Hon. Treasurer, D.J. Montier, Eyebrook, Oldfield Road, Bickley, Bromley, Kent. BR1 2LF, UK. COMMITTEE Dr C.F. Mann (Chairman) (2001) I.R. Bishop OBE (2003) Mrs M.N. Muller (2003) Vice-Chairman C.W.R. Storey (2003) S.A.H. Statham (Hon. Secretary) (2004) J.P. Hume (2004) D.J. Montier (Hon. Treasurer) (1997) Dr P.G.W. Salaman (Hon. Website Manager) (2001) Professor R. A. Cheke (BOC Publications) (2001) Ex-officio members Hon. Editor: G.M. Kirwan (1 January 2004) Chairman of BOU/BOC Joint Publications Committee (JPC): Reverend T.W. Gladwin. Membership Secretary: Cdr. M.B. Casement OBE RN (2004) Registered Charity No. 279583 Bulletin of the British Ornithologists’ Club ISSN 0007-1595 Edited by Guy M. Kirwan Volume 124, Number 2, pages 73-152 CONTENTS ll 9088 01058 Club Ammounceme nts 5. .....:..00ss..s.s0eedectuseasseneieseenaseanecesnsnerenonstbyadenceasitie seeneseas= sae eae eae aaa 73 WARAKAGODA, D. H. & RASMUSSEN, P. C. A new species of scops-owl from Sri Lanka ........ 85 WHITTAKER, A., ANTOINE-FEILL S., A. H. & SCHEIELE Z., R. First confirmed record of Oilbird Steatornis caripensis for Brazil ..............::.c-s0sseeercennesateesseeesodedustesenndennnucrssegen 106 BUCKLEY, P. A. & BUCKLEY, F. G. Rapid speciation by a Lesser Antillean endemic, Barbados Bullfinch Loxigilla Darbadensi5 ..........:.<.s0scssesssaeseaysecsssavasnssenssennesisannsesesciqnaeedeeinaeee 108 VELLINGA, W.-P., FLANAGAN, J. N. M. & MARK, T. New and interesting records of birds from Ayabaca province, Piura, north-west Peru. ..............i8b.:-.dsc0s & WNONN NN NY NN WYN HY ES Ke eK Se = GTO MON DUN BPWNrR COW WAND NA PW WV Localities, provinces Atacames—Tonsupa area, Esmeraldas Cerro Golondrinas Reserve, Carchi Guandera Biological Station, Carchi Alto Choco Reserve, Imbabura Finca Paraiso de Papagayos, Esmeraldas Los Cedros Reserve, Imbabura Laguna Grande, Cuyabeno Reserve, Sucumbios Palmitopamba, Pichincha Mindo, Pichincha Tandayapa Valley, Pichincha Oyacachi, Napo Oyacachi—El Chaco road, Napo Parque Metropolitano, Quito, Pichincha Papallacta, Napo Panacocha, Sucumbios Confluence of rio Paflayacu with rio Napo, Sucumbios Otonga Reserve, Cotopaxi Micacocha, Antisana Ecological Reserve, Napo Tiputini Biodiversity Station, Orellana Yasuni Research Station, Orellana Machay, Tungurahua Parque Omaere, Pastaza Cashca Totoras, Bolivar Tiquibuzo, Bolivar La Libertad, Guayas Unnsuants, Morona-Santiago Guarumales, Azuay Muiazal, Morona-Santiago Fasanan, Azuay Nueva Alianza, Morona-Santiago TINY HAWK Accipiter superciliosus One was observed and tape-recorded atop a Cecropia tree at a forest border at Tiputini Biodiversity Station, Orellana province, on 15 January 2000. It was giving a fast and agitated series of klee-e, klee-e calls (it also gave the same call described by Ridgely & Greenfield 2001), and had an antbird-sized bird in its claws. Another bird was observed at close range for c.5 minutes in primary forest edge at Yasuni Research Station, on 27 September 2001. Both localities are within Yasuni National Park. On 4 September 2000, at Miazal, Morona-Santiago province (trans-Kutuku region), 300 m elevation, two birds were also seen at a forest border perching at Co-ordinates 00°52’N, 79°51’W 00°49’N, 78°07’ W 00°36’N, 77°41’W 00°22’N, 78°27’ W 00°18’N, 79°27’W 00°18’N, 78°46’ W 00°02’N, 76°12’W 00°10’N, 78°40’ W 00°02’S, 78°48’ W 00°01°S, 78°46’W 00°05’S, 78°34" W 00°14’S, 77°55’°W 00°13’S, 78°30’W 00°22’S, 78°13’W 00°23’S, 76°07’ W 00°26’S, 76°05’ W 00°25’S, 79°00’ W 00°30’S, 78°08’ W 00°38’S, 76°08’ W 00°40’S, 76°23’ W 01923735, 7S ww. 01°28 Sires 01°43’S, 78°58’ W 02°01’S, 79°05’ W 02°14’S, 80°577W 02°33"S, 77°54ai 02°34’S, 78°30°W 02°38’S, 77°477W 03°02’S, 78°42’W 02°05’S, 78°09" W Altitude (m) 10 1,900 3,600 2,100 100 1,450 220 1,400 1,500 1,800 3,000 2,550 2,900 3,600 220 200 1,750 3,800 200 220 Juan F. Freile 191 Bull. B.O.C. 2004 124(3) canopy level and giving a weak cree-cree call (see Ridgely & Greenfield 2001). There are few records of this species in Amazonian Ecuador (Ridgely & Greenfield 2001), where it appears to be a widespread, low-density resident (R. S. Ridgely pers. comm. ). MERLIN Falco columbarius A single was observed at close range for up to 15 minutes above Papallacta, Napo province, at 3,600 m elevation on 28 January 2002, flying above paramo and actively chasing and attacking a flock of Brown-bellied Swallows Notiochelidon murina. At Guandera Biological Station, Carchi province, two individuals were observed on two separate occasions, on | and 3 February 2002, flying over paramo and adjacent elfin forest at 3,500—3,600 m elevation. This migrant raptor was previously reported up to 3,000 m (Ridgely & Greenfield 2001) and was not recorded at Guandera by Cresswell ef al. (1999) (although their study was undertaken in July-September, when the species would not be present). D. Wolf (pers. comm. to R. S. Ridgely) also recorded this species above Papallacta on 16 January 2000, suggesting that it may be regular there. WHIMBREL Numenius phaeopus A single was observed at close range for several minutes at a swampy area in the paramo of Guandera Biological Station, Carchi province, at 3,600 m elevation. This species was previously recorded primarily from the coastal lowlands in Ecuador, with only a handful of records inland, including a single record from the highlands (Ridgely & Greenfield 2001). Confusion with other shorebird species is unlikely, as the long decurved bill and bold stripes in the crown are unique among other species occurring in Ecuador (Hayman ef al. 1996, Ridgely & Greenfield 2001). WHITE-RUMPED SANDPIPER Calidris fuscicollis One was observed closely feeding at a sandy beach and in flight at the rio Esmeraldas, below Finca Paraiso de Papagayos (3 km by road from Quinindé town), at c.100 m elevation, on 10 March 1998. It was identified in flight by its conspicu- ous white rump, a feature not present in any other sandpiper species that occurs regularly in Ecuador (Hayman ef al. 1986, Ridgely & Greenfield 2001). Curlew Sandpiper Calidris ferruginea, an Old World species that has been recorded once in Ecuador (Ridgely & Greenfield 2001), has a long and slightly down-curved bill and long legs (protruding in flight) (Hayman ef a/. 1986), two features not shown by the observed bird. There are very few records of this species in Ecuador and none from the western lowlands (Ridgely & Greenfield 2001). As it does not winter in Ecuador (Ridgely & Greenfield 2001) this record probably involved a bird returning to its breeding grounds from southern South America (Hayman ef al. 1986). PECTORAL SANDPIPER Calidris melanotos A flock of 4-5 was observed at a muddy area next to Micacocha Lake, Antisana Ecological Reserve, Napo province, at 3,800 m elevation, on 24 September 1997. Juan F. Freile 192 Bull. B.O.C. 2004 124(3) Identification was based on throat and breast streaking abruptly ending on the lower breast. One of the observers (P. Catry) had extensive experience with shorebird identification and confirmed its identity. Previously recorded up to 3,500 m in Ecuador (Ridgely & Greenfield 2001). STILT SANDPIPER Micropalama himantopus Two were observed in a flock including Greater Tringa melanoleuca and Lesser Yellowlegs T: flavipes, and Spotted Actitis macularius and Baird’s Sandpipers Calidris bairdii, at Micacocha Lake, Antisana Ecological Reserve, Napo province, at 3,800 m elevation, on 24 September 1997. All were feeding along a muddy beach and floating vegetation of this lake. The Stilt Sandpipers were identified by their long whitish superciliary stripes, long slightly curved bill and long greenish legs (Hayman et al. 1986, Ridgely & Greenfield 2001). Previously known from two other Andean localities in Ecuador up to 3,500 m (Ridgely & Greenfield 2001). WILSON’S PHALAROPE Phalaropus tricolor Three were observed feeding on floating vegetation at Micacocha Lake, Antisana Ecological Reserve, Napo province, at 3,800 m elevation, on 24 September 1997. This species was previously reported up to 3,500 m in Ecuador (Ridgely & Greenfield 2001). Subsequently, this area has been dammed, a change that will probably reduce the number of visiting migrant shorebird species, as well as of resident waterbirds in the near future (e.g. Silvery Grebe Podiceps occipitalis, Black-faced Ibis Theristicus melanopis) that were associated with this lake (however see Munoz & Olmedo 2001). RED-AND-GREEN MACAW 4ra chloropterus A flock of five was observed over primary forest and forest border above Tiputini River, at Tiputini Biodiversity Station, Yasuni National Park, at 250 m elevation, on 17 January 2000. Another flock of four was observed flying over Panacocha Lake and adjacent primary forest, Sucumbios province, at a similar altitude, on 25-26 January 2000. Ara chloropterus is seemingly declining in Ecuador with only few recent records, and an apparent absence from seemingly adequate habitat (Ridgely & Greenfield 2001, Ribadeneira 2002). GOLDEN-PLUMED PARAKEET Leptosittaca branickii Two flocks of c.10 individuals in each were recorded daily (one of them was tape- recorded) at Fasafian (upper rio Shiu), Azuay province, between 2,900 and 3,100 m elevation, on 16—21 December 1999. Forest at these altitudes is fairly continuous at Fasanan, and comprises at least 600 ha (Freile 2000). There is a good number of recent records of this threatened species in southern Ecuador, which apparently engages in seasonal migrations (Ridgely & Greenfield 2001). These latter authors suggest that L. branickii is probably not so gravely at risk, but its geographic restric- tion, nomadic behaviour and the fact that during breeding the species becomes very Juan F. Freile 193 Bull. B.O.C. 2004 124(3) local and vulnerable to poaching should be taken into account to better assess its conservation status (Jacome 2002, N. Krabbe pers. comm.). RED-FACED PARROT Hapalopsittaca pyrrhops A pair was observed on two separate days flying above montane forest and adjacent clearings at Fasanan, Azuay province, at 3,000 m elevation, on 17 and 19 December 1999. The species is known from a handful of sites in southern Ecuador, and is threatened by intense deforestation throughout its small range (BirdLife International 2000, Ridgely & Greenfield 2001). For natural history information see Toyne eft al. (1995) and Toyne & Flanagan (1997). RED-BILLED PARROT Pionus sordidus A single bird was observed flying above forested and cleared areas at Cashca Totoras, Bolivar province, at 2,900—3,000 m elevation, on 7 September 1999. It was readily identified from White-capped Parrot, Pionus seniloides, the only other parrot species recorded at this site, by its uniformly green-coloured plumage, red vent and reddish bill (Ridgely & Greenfield 2001). It was not seen during the following days, suggesting that it was only passing through the area. However, three additional birds were observed by E. Bonaccorso in July 2003. It was previously reported up to 2,600 m in the eastern slope of the Andes in Ecuador (Ridgely & Greenfield 2001). There are some other records of local migrations in this species (Forshaw & Cooper 1977) but it has also been suggested that it is poorly adapted for long-distance daily movements (Collar 1997). BAND-BELLIED OWL Pulsatrix melanota Up to five individuals were heard, seen and tape-recorded at primary forest borders and adjacent clearings with tall standing trees in Nueva Alianza, Morona-Santiago province, at 1,300—1,500 m elevation, on 11—19 May 2002. This owl was previously unrecorded from the central portion of the eastern Andean slope, and this record helps partially to fill this discontinuity (Ridgely & Greenfield 2001). SHORT-EARED OWL Asio flammeus One was observed during late afternoon perching on a fence post and flying over agricultural fields for c.20 minutes in Tiquibuzo, Bolivar province, at 2,200 m altitude, on 31 October 1999. Previously recorded mostly between 3,000 and 4,000 m along the Andes of Ecuador (Ridgely & Greenfield 2001). COLLARED INCA Coeligena torquata Four were observed feeding on an unidentified Rubiaceae sp. and chasing other hummingbirds inside secondary forest above Machay, Tungurahua province, at 1,800 m elevation, on S—9 August 1999. Previously recorded mostly between 2,100 and 3,000 m (Krabbe et a/. 1998, Ridgely & Greenfield 2001), but now regularly found down to 1,750 m at Tandayapa, Pichincha province, mainly at bird feeders (R. S. Ridgely pers. comm.). Furthermore, at least three individuals were observed in Juan F. Freile 194 Bull. B.O.C. 2004 124(3) secondary forest and at forest borders in Tiquibuzo, Bolivar province (2,200 m), on 30 October—3 November 1999. Recent records of this species in western Ecuador are restricted to the north (south to Cotopaxi province, Ridgely & Greenfield 2001). EMERALD TOUCANET Aulacorhynchus prasinus Heard and seen within secondary forest and forest borders above Machay, Tungurahua province, at 1,600—1,800 m elevation, on 5—9 August 1999. Birds showed a contrasting whitish throat and yellow central stripe on their bills, two features that distinguish the race albivitta, of northern Ecuador and eastern Colombia, from the southern race cyanolaemus (Ridgely & Greenfield 2001). This record extends the currently known range of albivitta by c.60 km south to the northern side of the Pastaza River depression, and fills an apparent discontinuity in the distribution of A. prasinus (Ridgely & Greenfield 2001). The rio Pastaza appears to constitute a distributional barrier for some Andean taxa (e.g. Moustached Antpitta Grallaria alleni, Handsome Flycatcher Myiophobus pulcher; see Krabbe et al. 1998), and it also separates the ranges of subspecies that may actually represent valid species (e.g. Metallura williami, see Krabbe et al. 1998, Ridgely & Greenfield 2001). It seems plausible that the rio Pastaza also separates the races of A. prasinus, but confirmation of which race occurs in the intervening area between Tungurahua and Morona-Santiago provinces is needed. As suggested by Ridgely & Greenfield (2001) and Navarro et al. (2001) this species with many allopatric taxa may prove to be separable into different valid species. BLACK-BILLED MOUNTAIN-TOUCAN Andigena nigrirostris A group of five was observed daily at a campsite in Oyacachi—El Chaco road, Napo province, at 2,550 m elevation on 17—22 February 1997. Grey-breasted Mountain- toucan A. hypoglauca was not recorded at the site. A. nigrirostris was previously known up to 2,300 m altitude, above which it is replaced by Grey-breasted Mountain-toucan (Krabbe et al. 1998, Ridgely & Greenfield 2001). CHANNEL-BILLED TOUCAN Ramphastos vitellinus Two were heard, seen and tape-recorded at a primary forest border in Nueva Alianza, Morona Santiago province, at 1,500 m elevation, on 18 May 2002. This Amazonian species has been found as high as 1,400 m in the Cordillera de Kutuku and locally up to 1,100 m along the Andean foothills (Ridgely & Greenfield 2001). CHESTNUT-MANDIBLED TOUCAN Ramphastos swainsonii Two were observed and heard daily at a campsite located in secondary forest at 1,400 m elevation in Palmitopamba, north-west of Nanegal, Pichincha province, on 22-26 July 1996. Additionally, several were observed in secondary forest, forest borders and adjacent clearings with tall standing trees in Los Cedros Reserve, Imbabura province, at 1,400—-1,500 m elevation, on 17-23 May 1999. Ridgely & Greenfield (2001) reported old records at similar altitudes in the north-west, but gave recent records only as high as 1,000 m, in south-western Ecuador. Juan F. Freile 195 Bull. B.O.C. 2004 124(3) OLIVACEOUS PICULET Picumnus olivaceus One was observed at close range feeding along vines and small trees in secondary forest at 1,400 m elevation in Palmitopamba, north-west of Nanegal, Pichincha province, on 24 July 1996. Previously recorded mainly below 900 m (Ridgely & Greenfield 2001). LINED ANTSHRIKE TJhamnophilus tenuepunctatus Several were heard, seen and tape-recorded at secondary forest, forest borders, gardens and shrubs in adjacent clearings in Guarumales (Hidropaute Company Camp), Azuay province, at 1,750 m elevation, on 2—7 December 1999. Previously known to occur mostly below 1,400 m (Rassmusen & Rahbek 1994, Ridgely & Greenfield 2001), with small numbers up to 1,650—1,700 m in Zamora-Chinchipe (R. S. Ridgely pers. comm.). Ridgely & Greenfield (2001) suggested that this species may be spreading upslope following deforestation. WHITE-BACKED FIRE-EYE Pyriglena leuconota A male was mist-netted and collected in Palmitopamba, north-west of Nanegal, Pichincha province, on 25 July 1996, at 1,450 m elevation. The specimen was deposited at the Zoology Museum of the Departamento de Biologia, Pontificia Universidad Catolica del Ecuador (QCAZ 1289). In the western Andes of Ecuador P. leuconota had not previously been recorded above 1,350 m, at nearby Maquipucuna Reserve (Ridgely & Greenfield 2001). SPOTTED TODY-FLY CATCHER Jodirostrum maculatum One was observed closely for c.5 minutes in an /nga sp. planted tree in the gardens of Yasuni Research Station, Orellana province (250 m elevation), on 20 January 2000. Another was observed and tape-recorded in a garden bush in Pafiacocha, Sucumbios province (c.250 m), on 23 January 2000. It was readily identified by the spotted pattern on the white throat and yellow breast and sides, and by the contrast- ing grey head and conspicuous pale orange iris (Ridgely & Tudor 1994, Ridgely & Greenfield 2001). These authors mentioned that in Ecuador T. maculatum has been recorded only on river islands and riparian woodland along the lower section of the Napo, Aguarico and Pastaza rivers. My records might represent dispersing or wandering individuals, which had followed the courses of small tributaries of the Napo River (Tiputini and Panayacu), or that the species is beginning to spread into anthropogenic habitat (R. S. Ridgely pers. comm.). PIED WATER-TYRANT Filuvicola pica One was observed on a sandy shore and adjacent vegetation at the confluence of the Panayacu with the Napo, Sucumbios province, on 30 January 2000. The black-and- white plumage pattern was conspicuous and distinctive. There is only one previous record in Ecuador, also from along the Napo but several km upstream, in the Jatun Sacha area (Ridgely & Greenfield 2001). Its status here remains uncertain. Juan F. Freile 196 Bull. B.O.C. 2004 124(3) YELLOW-BELLIED CHAT-TYRANT Ochthoeca diadema A single was observed and tape-recorded in secondary forest undergrowth dominated by bamboo in Tiquibuzo, Bolivar province (2,200 m elevation), on 2 November 1999. On the western slope of the Andes the species has been recorded south to Cotopaxi province in the north, and locally in the south-west, in Azuay province (Ridgely & Greenfield 2001). Tiquibuzo is located c.120 km north of the Azuay site and c.140 km south of western Cotopaxi, but this record accords with the range estimation given by Krabbe et al. (1998), and helps to fill the apparent gap between the two areas (its distribution is probably continuous in appropriate habitat). STRIPED MANAKIN Machaeropterus regulus A female was mist-netted and photographed within secondary forest in Parque Omaere (near El] Puyo), Pastaza province, at 950 m elevation, on 13 November 1999. This Amazonian manakin has been reported up to 1,000 m in the south-east (Cordillera de Kutuku), but in the north it is not usually found above 700 m (Ridgely & Greenfield 2001). This is the highest record from north of the Pastaza River. BEAUTIFUL JAY Cyanolyca pulchra A group of six was observed and tape-recorded inside secondary forest along a creek in the Cerro Golondrinas Reserve, Carchi province, at 1,900 m altitude, on 2 June 1999. This restricted-range and Near-Threatened species is known from only a few localities in Ecuador, and is apparently declining (Ridgely & Greenfield 2001, Greenfield 2002). RED-EYED VIREO Vireo olivaceus Three different observers (J. A. Chaves, P. Castafieda and the author) observed a group of three birds during the morning of 22 March 2002 in Quebrada Ashintaco, Parque Metropolitano, Quito, Pichincha province, at 2,900 m elevation. They were feeding and moving conspicuously among shrubby vegetation. They were not observed subsequently, so they probably represented the boreal migrant olivaceus race, which is the only subspecies of V olivaceus recorded in the highlands of Ecuador (Ridgely & Greenfield 2001). There is a single highland record from southern Ecuador, and it has not been previously found in the Quito area (Ridgely & Greenfield 2001). BLACK-BILLED THRUSH Turdus ignobilis Several were observed along forest borders and open areas around Machay town, Tungurahua province, at 1,600 m elevation, on 5 August 1999. On 2-7 December 1999, in Guarumales, Azuay province (1,750 m), several were also seen and heard in open areas, gardens and adjacent secondary forest. Previously recorded up to 1,200 m, but as this species is capable of quickly colonising recently cleared areas Juan F. Freile 197 Bull. B.O.C. 2004 124(3) it is not unexpected to find it at open areas above this elevation (Ridgely & Greenfield 2001). SOUTHERN ROUGH-WINGED SWALLOW Stelgidopteryx ruficollis Singles, small groups and large flocks of this species have been recorded at altitudes above those reported by Ridgely & Greenfield (2001). Records come from Cerro Golondrinas Reserve (1,700—1,800 m), Bellavista Reserve (1,800 m), Tandayapa Bird Lodge (1,700 m), Mindo Biological Station (1,700 m) and Otonga Reserve (1,700—1,800 m). As this species is capable of long flights, and is also typical of cleared areas, it may be spreading upslope following deforestation. GRASS WREN Cistothorus platensis At least two were heard and seen in artificial pastures at 1,900 m elevation above Guarumales Camp, Azuay province, on 2 December 1999. The species is known to occur mostly above 2,800 m, with a few records down to 2,200 m (Loja—Zamora road) (Ridgely & Greenfield 2001). Considering the extent of pastureland along the road from Paute through Guarumales (pers. obs.), it seems plausible that this species is spreading downslope following deforestation. TENNESSEE WARBLER Vermivora peregrina One was mist-netted and released in a shrubby creek surrounded by planted Eucalyptus Eucaliptus globulus trees in Parque Metropolitano, outside Quito, Pichincha province, at 2,900 m elevation, on 6 March 2002. This migrant species has been previously reported from a single inter-Andean locality (San Pablo Lake) and at present is mostly known from the western slope of the Andes, in the Mindo area (Ridgely & Greenfield 2001), with an additional recent record from Bombuscaro, Podocarpus National Park, Zamora-Chinchipe province (N. Athanas pers. comm. to R. S. Ridgely). AMERICAN REDSTART Setophaga ruticilla Several were observed and heard giving soft scheet calls in secondary forest and adjacent gardens in Parque Omaere (near El Puyo), Pastaza province, at 950 m elevation, on 11-14 November 1999. In eastern Ecuador S. ruticilla is known to occur along the entire base of the Andes (Ridgely & Greenfield 2001), although the distribution map in this work does not include the area. CANADA WARBLER Wilsonia canadensis One was mist-netted and photographed in a regenerating scrubby area adjacent to secondary forest at a campsite on the Oyacachi—E] Chaco road, Napo province, at 2,550 m elevation, on 19 February 1997. Previously recorded from both sides of the Andes up to 2,000 m (Ridgely & Greenfield 2001). Juan F. Freile 198 Bull. B.O.C. 2004 124(3) BUFF-RUMPED WARBLER Basileuterus fulvicauda Three were observed in shrubby vegetation along a small stream in secondary forest at c.1,600 m elevation in the Cerro Golondrinas Reserve, Carchi province, on 1 June 1999. It had previously been recorded only below 1,000 m (Ridgely & Greenfield 2001). CHESTNUT-VENTED CONEBILL Conirostrum speciosum One male was observed for c.5 minutes in a primary forest border at Laguna Grande Lake, Cuyabeno Faunistic Reserve, Sucumbios province, 220 m elevation, on 14 September 1996. It was identified by its bluish-grey plumage with a conspicuous chestnut vent and by the small whitish spot in the wing (which was fairly conspic- uous in the individual observed) (Hilty & Brown 1986). Confusion with other passerines was unlikely (see Hilty & Brown 1986, Ridgely & Greenfield 2001). There is only a handful of previous records in Ecuador, all of them above 400 m elevation, near the base of the Andes (Ridgely & Greenfield 2001). It is regular around and just above the town of Zamora, often feeding in Jnga sp. trees (R. S. Ridgely pers. comm.). This species was reported as a rare inhabitant at the margins of lakes in the Cuyabeno area by Paz y Mifio (1989); however he did not provide any further details of his observations. This record is the first modern report away from the Andean foothills. GOLDEN-RUMPED EUPHONIA Euphonia cyanocephala A group of three was observed at close range accompanying a mixed-species flock, mainly of tanagers, in a shrubby area in Oyacachi town, Napo province 3,000 m elevation, on 15 February 1997. This report represents the highest elevation at which this species has been recorded in Ecuador (R. S. Ridgely pers. comm.). This handsome euphonia occurs mostly along the west slope of the Andes and the inter- Andean valleys, with only scattered records from the eastern slope (Ridgely & Greenfield 2001). Eastern records come from areas altitudinally below Oyacachi (San Isidro, Valladolid, Machay; Ridgely & Greenfield 2001). BLACK-CAPPED TANAGER Tangara heinei A pair was observed feeding at an isolated Moraceae tree in a degraded area close to secondary forest, and attending a nest in the same tree, in Alto Choco Reserve (on the road to Intag), Imbabura province, at 2,100 m elevation, on 16—20 June 1999. I was unable to see if the nest already contained eggs or nestlings, but nest material (small thin twigs) was frequently transported by both birds to the nest site. The species has been recorded from a few sites in western Ecuador, all of them recent, mostly between 1,100 and 1,900 m elevation (Ridgely 1980, Ridgely & Greenfield 2001). SILVER-BEAKED TANAGER Ramphocelus carbo Several were observed along forest borders, clearings and gardens at two sites in the eastern slope of the Andes: Machay town, Tungurahua province, at c.1,600 m Juan F. Freile 199 Bull. B.O.C. 2004 124(3) elevation, on 5 August 1999, and Guarumales Camp, Azuay province, at 1,700 m, on 2—7 December 1999. Previously recorded up to 1,300 m in western Napo (Ridgely & Greenfield 2001). It has also been recorded in recent years up to 1,600 m in Valladolid, Zamora-Chinchipe province (R. S. Ridgely pers. comm.). This species is capable of rapidly colonising recently cleared areas, and its presence at both sites reported here is not surprising. RED-HOODED TANAGER Piranga rubriceps Two were observed at a secondary forest gap close to a forest border, at 1,700 m elevation, above Machay, Tungurahua province, on 7 August 1999. This striking tanager has been recorded mostly between 2,200 and 3,000 m altitude and seems to occur continuously along the eastern slope of the Andes in Ecuador (Krabbe et al. 1998, Ridgely & Greenfield 2001). BLACK-EARED HEMISPINGUS Hemispingus melanotis ochraceus One was mist-netted and photographed in secondary forest dominated by bamboo in the Cerro Golondrinas Reserve, Carchi province, at 2,000 m altitude, on 4 June 1999. The species is known from very few sites in north-west Ecuador, all of them from Pichincha south to Azuay province (Ridgely & Greenfield 2001). The present site is c.80 km north of previously known sites, but is in accordance with the estimated geographic range made by Krabbe et al. (1998). My record also partially fills the apparent discontinuity between Pichincha and south-west Colombia, where it has also been found (Hilty & Brown 1986). The race ochraceus was recently proposed to represent a separate species (Ridgely & Greenfield 2001), but molecu- lar data do not support this assumption (Garcia-Moreno et al. 2001, 2003). ROSE-BREASTED GROSBEAK Pheucticus ludovicianus One was observed within a mixed-species flock in a shrubby area adjacent to secondary forest in Guarumales Camp, Azuay province, at 1,750 m altitude, on 5 December 1999. Records of this migrant species come mostly from western Ecuador, with only a few reports from the eastern slope of the Andes (Ridgely & Greenfield 2001). YELLOW-FACED GRASSQUIT Tiaris olivacea A group of c.5 individuals was observed on 11—14 September 1999, in the Atacames-Tonsupa area, Esmeraldas province. This is the first record from coastal Ecuador (Ridgely & Greenfield 2001). The species, considered a recent arrival by Ridgely & Greenfield (2001), seems to be spreading in western Ecuador following deforestation and will probably be encountered in other areas further south, west and north. LESSON’S SEEDEATER Sporophila bouvronides Flocks of up to seven (males and female-plumaged birds) were observed in small pastures along the Maxus Road, Yasuni National Park, Orellana province, at the Ce eS UN Ne aa Juan F. Freile 200 Bull. B.O.C. 2004 124(3) following sites: Capiron, YPF Camp, Amo-C Camp and Yasuni Research Station, in June 1998 and 2000. The status of this intratropical migrant species in Ecuador is still poorly known, with only a few scattered records mostly from November to April (Ridgely & Greenfield 2001). The records reported here are anomalous, as is the August record mentioned by Ridgely & Greenfield (2001). Although S. bouvronides can easily be confused with S. lineola (Lined Seedeater), none of the males observed had the white coronal stripe typical of the latter species (see Hilty & Brown 1986, Ridgely & Greenfield 2001). YELLOW-BROWED SPARROW 4Ammodramus aurifrons Several were seen and tape-recorded at clearings and gardens in Guarumales Camp, Azuay province, at 1,750 m altitude, on 2-7 December 1999. This species seems to be spreading to Andean slopes following deforestation, as it is able to colonise newly cleared areas quickly (Ridgely & Greenfield 2001). It has previously been recorded up to 1,600 m, and even to 2,500 m as a wanderer (Ridgely & Greenfield 2001). At present it is also common around Valladolid, Zamora-Chinchipe province, at 1,600 m elevation (R. S. Ridgely pers. comm.). GREAT-TAILED GRACKLE Quiscalus mexicanus Groups and singles were observed at La Libertad town, Guayas province, on the Santa Elena Peninsula, on 28—31 August 2001. Previous records in western Ecuador were restricted to areas where mangroves are still extensive (Ridgely & Greenfield 2001), and these authors mentioned that in the Santa Elena Peninsula it does not occur at all. The birds observed were probably dispersing from other areas further north or, even more likely, this species is beginning to colonise anthropogenic areas, as it does in other countries. Acknowledgements I thank Tom B. Smith, Borja Mila and Jordan Karubian, Center for Tropical Research, University of California at Los Angeles for letting me publish bird records gathered during their field research in Ecuador (Nueva Alianza, Tiputini, Yasuni, Miazal, Pafacocha, Parque Metropolitano), to Felipe Campos and Andrés Vallejo, Centro de Datos para la Conservacion—Ecuador (CDC—Ecuador), for taking me on field trips to Palmitopamba and Oyacachi, to Tjitte de Vries (Departamento de Biologia, Pontificia Universidad Catolica del Ecuador) and Milton Ortega (Daimi Services) for the trips to Yasuni National Park, and to Isidro Gutiérrez at Ministerio del Ambiente for research permits for visiting other sites (see Freile 2000). Field research in other areas was financially supported by Programa de Becas de Investigacion para la Conservacion of Fundacion EcoCiencia (funds from a grant of the Royal Embassy of the Netherlands), and the William Belton Donation Program of American Bird Conservancy. Several people and institutions gave logistic support and are fully acknowledged in Freile (2000). I also thank all the people who have accompanied me on field trips, particularly Melissa Moreano, Jaime A. Chaves, Nadia Vieira, Santiago Espinosa, David Lasso, Miguel Pinto, Gustavo Cafias and Paulo Catry. Mark B. Robbins, Robert S. Ridgely and Niels Krabbe are deeply thanked for their comments on this manuscript, and Kerem Ali Boyla for preparing the map. This paper is dedicated to the late Fernando Ortiz-Crespo for sharing his enthusiasm for and knowledge of birds. Juan F. Freile 201 Bull. B.O.C. 2004 124(3) References: BirdLife International. 2000. Threatened birds of the world. BirdLife International, Cambridge, UK & Lynx Edicions, Barcelona. Collar, N. J. 1997. Family Psittacidae (Parrots). Pp. 280-477 in del Hoyo, J., Elliott, A. & Sargatal, J. (eds.). Handbook of the birds of the world, vol. 4. Lynx Edicions, Barcelona. Collar, N, J., Crosby, M. J. & Stattersfield, A. J. 1994. Birds to watch 2: the world list of threatened birds. BirdLife International, Cambridge, UK. Cresswell, W., Mellanby, R., Bright, S., Catry, P., Chaves, J., Freile, J., Gabela, A., Hughes, M., Martineau, H., Macleod, R., McPhee, F., Anderson, N., Holt, S., Barabas, S., Chapel, C. & Sanchez, T. 1999. Birds of the Guandera Biological Reserve, Carchi province, north-east Ecuador. Cotinga 11: 55-63. Forshaw, J. M. & Cooper, W. T. 1977. Parrots of the world. T. F. H. Publications, Neptune City, NJ. Freile, J. F 2000. Patrones de distribucion y sus implicaciones en la conservacion de los géneros Grallaria y Grallaricula (Aves: Formicariidae) en el Ecuador. Tesis de Licenciatura, Departamento de Biologia, Pontificia Universidad Catolica del Ecuador, Quito, Ecuador. Garcia-Moreno, J., Ohlson, J. & Fjeldsa, J. 2001. MtDNA sequences support monophyly of Hemispingus tanagers. Mol. Phyl. & Evol. 21: 424-435. Garcia-Moreno, J. & Fjeldsa, J. 2003. Phylogenetic relationships among Hemispingus tanagers. Orn. Neotrop. 14: 363-370. Granizo, T., Pacheco, C., Ribadeneira, M. B., Guerrero, M. & Suarez, L. (eds.). 2002. Libro rojo de las aves del Ecuador. Simbioe, Conservation International, EcoCiencia, Ministerio del Ambiente & UICN, Quito. Greenfield, P. J. 2002. Cyanolyca pulchra. P. 325 in Granizo, T., Pacheco, C., Ribadeneira, M. B., Guerrero, M. & Suarez, L. (eds.) Libro rojo de las aves del Ecuador. Simbioe, Conservation International, EcoCiencia, Ministerio del Ambiente & UICN, Quito. Hayman, P., Marchant, J. & Prater, T. 1986. Shorebirds, an identification guide. Houghton Mifflin, Boston. Hilty, S. L. & Brown, W. L. 1986. A guide to the birds of Colombia. Princeton Univ. Press. Jacome, M. 2002. Leptosittaca branickii. Pp. 136-137 in Granizo, T., Pacheco, C., Ribadeneira, M. B., Guerrero, M. & Suarez, L. (eds.) Libro rojo de las aves del Ecuador. Simbioe, Conservation International, EcoCiencia, Ministerio del Ambiente & UICN, Quito. Joseph, L. 1997. Towards a broader view of Neotropical migrants: consequences of a re-examination of austral migration. Orn. Neotrop. 8: 31-36. Kirwan, G. M. & Marlow, T. 1996. A review of avifaunal records from Mindo, Pichincha Province, north-western Ecuador. Cotinga 6: 47-57. Krabbe, N., Poulsen, B. O., Fralander, A. & Rodriguez, O. 1997. Range extensions of cloud forest birds from the high Andes of Ecuador: new sites for rare or little-recorded species. Bull. Brit. Orn. C1.117: 248-256. Krabbe, N., Skov, F., Fjyeldsa, J. & Petersen, I. K. 1998. Avian diversity in the Ecuadorian Andes. An atlas of distribution of Andean forest birds and conservation priorities. DIVA Technical Report No. 4. Centre for Research on the Cultural and Biological Diversity of Andean Rainforests (DIVA), Ronde. Munoz R., I. & Olmedo G., I. 2001. Monitoreo de aves acuaticas y limnicolas en la laguna de la Mica y sus alrededores (Reserva Ecologica Antisana). Pp. 1-19 in Fundacion Antisana (ed.) Estudios biologicos de aves de altura: Reserva Ecologica Cayambe-Coca, R. E. Antisana. Serie Biorreserva del Condor No. 2. Proyecto Biorreserva del Condor, Quito. Navarro S., A. G., Peterson, A. T., Lopez-Medrano, E. & H. Benitez-Diaz. 2001. Species limits in Mesoamerican Aulacorhynchus toucanets. Wilson Bull. 113: 363-372. Paz y Mino, G. 1989. Lista anotada de algunas especies de aves comunes en la Reserva de Produccion Faunistica Cuyabeno, Amazonia del Ecuador. Fundacion Ornitologica del Ecuador, Quito. Rasmussen, J. F. & Rahbek, C. 1994. Aves del Parque Nacional Podocarpus, una lista anotada. Fundacion Ornitologica del Ecuador (CECIA), Quito. Juan F. Freile 202 Bull. B.O.C. 2004 124(3) Ribadeneira, M. B. 2002. Ara chloroptera. P. 234 in Granizo, T., Pacheco, C., Ribadeneira, M. B., Guerrero, M. & Suarez, L. (eds.) Libro rojo de las aves del Ecuador. Simbioe, Conservation International, EcoCiencia, Ministerio del Ambiente & UICN, Quito. Ridgely, R. S. & Tudor, G. 1994. The birds of South America, vol. 2. Univ. Texas Press, Austin. Ridgely, R. S. & Greenfield, P. J. 2001. The birds of Ecuador. Cornell Univ. Press, Ithaca, NY. Toyne, E. P. & Flanagan, J. N. M. 1997. Observations on the breeding, diet and behaviour of the Red- faced Parrot Hapalopsittaca pyrrhops in southern Ecuador. Bull. Brit. Orn. Cl. 117: 257-263. Toyne, E. P., Flanagan, J. N. M. & Jeffcote, M. T. 1995. Vocalizations of the endangered Red-faced Parrot Hapalopsittaca pyrrhops in southern Ecuador. Orn. Neotrop. 6: 125-128. Address: Numashir, Fundacion para la Conservacion de Ecosistemas Amenazados. Casilla Postal 17-12- 122, Quito, Ecuador, e-mail: jfreile@numashir.org © British Ornithologists’ Club 2004 First Palearctic record of the endangered Bermuda Petrel Pterodroma cahow by Foél Bried & Maria C. Magalhdaes Received 15 Fuly 2003 Many Procellariiformes make regular long-distance movements at sea (up to several thousands of km) during both breeding and non-breeding periods (Gonzalez-Solis et al. 2000, Weimerskirch et al. 1999, Weimerskirch & Wilson 2000). The Bermuda Petrel Pterodroma cahow, endemic to Bermuda (in the subtropical north-western Atlantic), is classified as Endangered according to IUCN Red List criteria (BirdLife International 2000), with a few tens of breeding pairs (BirdLife International 2000, Madeiros 2002). Its movements during the non-breeding period are poorly known, dispersal being supposed to occur towards the north or the north-west in the subtropical western Atlantic (del Hoyo et al. 1992), as far as off North Carolina (Wingate et al. 1998). Here, we report the first record of a Bermuda Petrel in the Palearctic. On 17 November 2002, during the daytime, MCM incidentally captured a gadfly petrel (genus Pterodroma) in a burrow on an offshore islet free of introduced predators, in the Azores archipelago. The bird was ringed using an individually numbered metal ring, measured and photographed (Figs. 1-3). Measurements taken were: wing length (flattened chord) using a stopped ruler correct to | mm; tarsus length; bill (exposed culmen length, bill depth at gonys, bill depth at nostrils) and total head length (head plus bill) using a vernier calliper (to 0.1 mm). A 100-ml blood sample was also taken (under license) for future genetic studies. The bird was released into its burrow after handling. Joél Bried & Maria C. Magalhdaes 203 Bull. B.O.C. 2004 124/3) The following description was taken. Upperparts dark to medium grey, gradually becoming blackish grey on nape and crown (Figs. | and 2); tail also dark grey but uppertail-coverts formed a narrow pale creamish, rather than greyish, crescent; forehead white with few black mottlings, the white almost extending to eyes; lores black near eye, white near bill and gape; ear-coverts black (Fig. 1). Underparts from chin to undertail-coverts, and flanks, pure white; sides of breast grey, but grey markings did not join to form a collar; no brood patch. Wings— upperwing dark grey without obvious markings (Fig. 2); axillaries white, marginal and lesser underwing-coverts blackish: lesser under secondary-coverts formed broad dark bar along forearm; median underwing-coverts white; greater underwing- coverts white but some dark spots visible in subterminal position on the greater TABLE 1 Measurements of Pterodroma cahow, P. feae and P. mollis. Mean values (and ranges in brackets) are given. All values are expressed in mm. Pcahow Pcahow’ Pcahow P feae P feae P feae P mollis dubia (Azores) (Bermuda) (Bermuda) (Azores) (Bugio) (Bugio) (Crozet) Wing 269" 260.7 ; (245-265) 269.75 267.8 266.4 248.2 (260-262) (269.5-270) (258-282) (262-270) (244-252) Tail - 120.9 ~ 120 110.3 108.5 1122 (118—123.8) (112-128) (106-155) (102-111) (108-116) Tarsus 35.9 35.4 ~ 35.3 35.8 35.9 36.8 (34.4-37.3) (35.0-35.6) (32.0-41.0) (34.3—38.2) (33.7-39.6) Culmen 28.3 28.6 28.1 29.1 29.1 28.4 28.4 (27.4-29.6) (25.7-304) (28.5-29.7) (27.0-31.0) (27.2—29.9) (27.1-29.3) Gonys 12.2 - 11.6 12.8 - 124 11.3 (10.7—12.3) (11.2—13.2) (10.3—12.0) Nostrils 14.0 - i124 13.0 14.6 14.3 13.0 (11.1—13.3) (13.0-16.2) (13.4—15.6) (12.1—14.8) Total head 75.6 — - 73.1 - 724 73.1 (71.3—73.3) (72.2-75.1) Middle toe — 47.1 - - - - plus claw (46.249.0) Sample size 1 3 8-11 1-2 29-40 3-5 4-11 Source® l 2 3 4,5 6 1 l 1 Flattened wing chord. 2 The sample included a fledgling. 31: this study (P feae and P mollis specimens are from the Muséum National d*Histoire Naturelle de Paris); 2: Murphy & Mowbray (1951, specimens); 3: Wingate ef al. (1998, specimens); 4: Bibby & del Nevo (1991. live bird); 5: Monteiro & Furness (1995, live bird); 6: Zino & Zino (1986, live birds). Joél Bried & Maria C. Magalhaes 204 Bull. B.O.C. 2004 124(3) Figure 1. Side view of the Bermuda Petrel captured in the Azores (J. Bried) Figure 2. Upperparts of the same individual (J. Bried) Figure 3. Underparts of the same individual (J. Bried) Joél Bried & Maria C. Magalhdes 205 Bull. B.O.C. 2004 124(3) under secondary-coverts and outermost greater under primary-coverts (Fig. 3). Legs pink; toes and webs with proximal third pink and distal two-thirds black, except for entirely black outer toe. Bill black with moderately arched maxillary unguis. This bird was clearly larger than Madeiran Petrel P madeira (see Monteiro & Furness 1995, p. 11) and slightly larger than Subantarctic Soft-plumaged Petrel P mollis dubia, but similar in size to Fea’s Petrel P feae (Table 1). Its measurements fell at the upper range limit for Bermuda Petrel specimens (Table 1), but well within the range of the values obtained from 12 live adults (J. L. Madeiros pers. comm.). The plumage characters of this bird, especially the underwing pattern with the dark ‘thumb print’ mark on the outer greater under primary-coverts and the pale band at the base of the tail (Wingate et a/. 1998), its measurements, and its more slender bill than in Fea’s Petrel (see, e.g. photograph in Monteiro & Furness 1995), confirmed it as Pterodroma cahow. This individual seemed robust and healthy. Although not weighed, a manual inspection showed that it was carrying fat reserves and had no apparent ectopara- sites. The petrel was recaptured in the same burrow on 21 November 2002 at c.22.00 h by JB after uttering a moaning call, apparently in response to the vocali- sations of a Little Shearwater Puffinus assimilis baroli in a neighbouring burrow. After we checked the ring number, the bird was again released into its burrow. During another visit to the islet on 31 January 2003, JB found the burrow empty and did not find Bermuda Petrels in any neighbouring burrows. Discussion Our capture of a Bermuda Petrel on 17 November 2002 represents, to the best of our knowledge, the first proven record of this species for the Palearctic. In addition, the recapture of this individual in the same burrow four days later suggests that it exhibited some level of site tenacity. The burrow was situated on a slope oriented eastwards, c.20 m above sea level. When breeding, Bermuda Petrels return ashore at the onset of the pre-laying period in late October and November; most eggs are laid during the first fortnight of January and chicks fledge in late May and June (Palmer 1962, del Hoyo ef al. 1992). The Azorean individual was thus occupying a burrow at the same period as its pre-laying conspecifics in Bermuda. This behaviour, together with its fat reserves, suggests that it was in pre-laying condition as well. In addition, its behaviour and its measurements (within the top 20% of the range) made it likely that it was a male (J. L. Madeiros & D. B. Wingate pers. comm.); however, this still needs confirmation through blood analyses. The scarcity of at-sea observations of Bermuda Petrel (Wingate et a/. 1998) makes it impossible to know whether or not the Azores area is part of the normal range of this species. Joél Bried & Maria C. Magalhaes 206 Bull. B.O.C. 2004 124(3) Acknowledgements This work was part of the Life Program “Gestao Integrada das Zonas Costeiras e Marinhas nos Acores’ (Contract B4-3200/98-509) and of JB’s post-doctoral contract IMAR/FCT-PDOC-001/2001-BirdEco. We thank V. Encarnacgao from CEMPA and the Direccgao Regional do Ambiente for allowing scientific work on the petrels in the Azores (Licence No. 4/CN/2002), as well as Marco and Zé Ricardo from the local Clube Naval for transportation to the islet. We are also grateful to the Muséum National d’ Histoire Naturelle de Paris (France) for allowing JB to examine specimens of Soft-plumaged and Fea’s Petrels, to J. L. Madeiros for providing us with measurements from live Bermuda Petrels, and to M. Bolton, D. B. Wingate and B. Zonfrillo for fruitful discussions via e-mail and/or help with the literature. M. Bolton additionally improved the English. We also thank C. Feare and an anonymous referee for their comments on the manuscript. References: Bibby, C. J. & del Nevo, A. 1991. A first record of Pterodroma feae from the Azores. Bull. Brit. Orn. Cl. 111: 183-186. BirdLife International. 2000. Threatened birds of the world. BirdLife International, Cambridge, UK & Lynx Edicions, Barcelona. Gonzalez-Solis, J., Croxall, J. P. & Wood, A. G. 2000. Sexual dimorphism and sexual segregation in ae aging strategies of Northern Giant Petrels, Macronectes halli, during incubation. Oikos 90: 390-398. del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 1992. Handbook of the birds of the world, vol. 1. Lynx Edicions, Barcelona. Madeiros, J. L. 2002. Bermuda’s remarkable Cahow. World Birdwatch 24: 16-18. Monteiro, L. R. & Furness, R. W. 1995. Fea’s Petrel Pterodroma feae in the Azores. Bull. Brit. Orn. Cl. 115: 9-14. Murphy, R. C. & Mowbray, L. S. 1951. New light on the Cahow, Pterodroma cahow. Auk 68: 266-280. Palmer, R. S. 1962. Handbook of North American birds, vol. 1. Yale Univ. Press, New Haven. Weimerskirch, H., Catard, A., Prince, P. A., Cherel, Y. & Croxall, J. P. 1999. Foraging White-chinned Petrels Procellaria aequinoctialis at risk: from the tropics to Antarctica. Biol. Conserv. 87: 273-275. Weimerskirch, H. & Wilson, R. P. 2000. Oceanic respite for Wandering Albatrosses. Birds taking time off from breeding head for favourite long-haul destinations. Nature 406: 955—956. Wingate, D. B., Hass, T., Brinkley, E. S. & Patteson, J. B. 1998. Identification of Bermuda Petrel. Birding 30: 18-36. Zino, P.A . & Zino, F. 1986. Contribution to the study of the petrels of the genus Prerodroma in the archi- pelago of Madeira. Bol. Mus. Mun. Funchal Suppl. 2: 325-331. Address: Departamento de Oceanografia e Pescas, Centro do IMAR da Universidade dos Agores, 9901- 862 Horta, Acores, Portugal, e-mail: joelbried@yahoo.com © British Ornithologists’ Club 2004 Guy M. Kirwan et al. 207 Bull. B.O.C. 2004 124(3) Further comments on the avifauna of the middle Sao Francisco Valley, Minas Gerais, Brazil by Guy M. Kirwan, Juan Mazar Barnett, Marcelo Ferreira de Vasconcelos, Marcos A. Raposo, Santos D’Angelo Neto & Ignacio Roesler Received 24 Fuly 2003 In earlier contributions (Kirwan ef al. 2001, Raposo et al. 2002, Whitney et al. 2003) GMK, JMB and others drew attention to the highly threatened avifauna of the middle reaches of the rio Sao Francisco in eastern Brazil, and the river’s importance in influencing biogeographical processes of avian speciation and endemism. We also presented notes on behavioural aspects of a number of poorly known species, and provided new southernmost records for several north-east Brazilian caatinga specialists. Details of our principal study sites were included in the earlier paper. Since then we have made further visits to the area, resulting in additional data substantially augmenting our previous field work. Here, our intention is only to supply details of those records that update our knowledge of the Minas Gerais avifauna, along the middle reaches of the Sao Francisco Valley. Systematic order and scientific nomenclature follow Sick (1997), with all departures from this explained in Kirwan et al. (2001). Methods All tape-recordings were made using Sony TCM-5000 EV tape recorders and Sennheiser ME-66 microphones, and will be deposited at the Arquivo Sonoro Prof. Elias Coelho (ASEC), Departamento de Zoologia, Universidade Federal do Rio de Janeiro, Rio de Janeiro, Brazil. Several ‘new’ localities were visited and details of these are presented below (see also Fig. 1). Coordinates were taken from GPS readings or estimated from a map. Rio Lavado (17°58’S, 44°34’W), Lassance municipality: a patch of gallery forest within an area of altered cerraddo (closed-canopy, dense woodland), south of Lassance, visited briefly on 9 January 2003. Lassance (17°54’S, 44°34°W), Lassance municipality: an area of cerrado and Mauritia palm veredas surrounding the city was visited on 2 February 1997. Fazendas Jatoba do Cotobelo and Jatoba da Mata (centred at 17°45’S, 44°42’W), Varzea da Palma municipality: possess areas of cerradado woodland, open areas with caatinga influence, and gallery forest, as well as wetlands and agricultural fields. Active carbon ovens were noted in the area. Visited on 10 January 2003. Guy M. Kirwan et al. 208 Bull. B.O.C. 2004 124(3) BRAZIL O Belo Horizont Figure 1. Map of the study localities in northern Minas Gerais. 1. Faz. Nova Uniao; 2.Japoré; 3. Mocambinho; 4. Peruagu; 5. Levindpolis; 6. Brejo do Amparo; 7. Januaria (10 km north of); 8.Po¢go da Vovo; 9. Pesqueiro Itambé; 10. rio Sao Francisco; 11. Faz. Buriti; 12. Curral de Pedras; 13. Serra Boqueirao; 14. Pirapora (south of); 15. Cia Florestal; 16. Faz. Jatoba do Cotovelo and Faz. Jatoba da Mata; 17. Lassance; 18. rio Lavado. Companhia Florestal at Varzea da Palma (centred at 17°40’S, 44°44’W), Varzea da Palma municipality: road south and west of the town, that passed through a forestry plantation (mainly Eucalyptus), and continued through areas of degraded cerraddo, open areas with influence of caatinga, and several tracts of gallery forest. Visited on 10 January 2003. Pirapora (south of) (centred at 17°25’S, 44°48’ W), Pirapora municipality: an area crossed by several minor roads south of the town, through caatinga—cerradao transi- tion habitats, open agricultural fields and a few remaining patches of tall woodlands. Visited on 11 January 2003. Serra do Boqueirao (17°23’S, 44°32’ W), Jequitai municipality: rocky escarpment between Jequitai and Varzea da Palma, accessed via a minor road. The area presents mostly degraded woodland and cerraddo habitats, agricultural fields, and taller woodland along the base of the serra. There is a large marshy area, as well as a number of small streams with narrow belts of gallery forest. Accessed from Jequitai on 11 January 2003. Curral de Pedras (17°06’S, 44°35’W), Jequitai municipality: north-east of Pirapora inland of the right bank of the Sao Francisco, accessed from Jequitai. The name, ‘curral de pedras’, refers to a limestone formation, which appears labyrinthine due to a series of concentric circles in the rock, and in this case is Guy M. Kirwan et al. 209 Bull. B.O.C. 2004 124(3) surrounded by reasonably well-preserved semi-deciduous dry forest. It was visited in late-November 1995. Fazenda Buriti (16°08°S, 45°09’ W), Pintopolis municipality: area of cerrado and pastures. Visited on 17 June 2002. Sao Francisco river (c.15°37°S, 44°28’ W), Januaria municipality: 15—20 km south of Januaria, along a dirt road parallel to the left margin of the river. It contains dense scrub, inundated areas and patches of tall gallery woodlands. It was visited on 10 February 2002, and on 13 and 15 January 2003. Brejo do Amparo (15°29’S, 44°22’W), Januaria municipality: a well-known locality (Snethlage 1928, Willis & Oniki 1991), c.10 km west of Januaria. We briefly surveyed the tall woodlands and fields along the rocky escarpments west of this locality, on 12 January 2003. Januaria (north of; c.15°25’S, 44°35’W), Januaria municipality: access roads to the “Escola Agrotécnica’, where areas of scrub among agricultural land, and patches of tall woodlands were surveyed on 14 January 2003. Poco da Vové (15°22’S, 43°37’W), Jaiba municipality: region of second-growth caatinga woodlands and pastures. It was visited on 7 July 2002. Pesqueiro Itambé (15°21°S, 44°11’ W), Januaria municipality, is located close to Riacho da Cruz village, at the left margin of rio Sao Francisco. Typical habitats are second-growth gallery forest, and riverbanks. This area was surveyed on 27-28 April 2002. Levinopolis (c.15°15’S, 44°17’W), Levinopolis municipality: area west of town, along a local road, through limestone escarpments with mostly low-stature (possibly degraded) semi-deciduous woodlands. Visited on 14 January 2003. Japoré (14°42’S, 44°04°W), Manga municipality: second-growth caatinga woodland. Visited on 6 July 2002. Fazenda Nova Uniao (14°25’S, 44°26’ W), Montalvania municipality: 1.5 km north of Montalvania, the fazenda contains arboreal caatinga, second-growth caatinga woodland, and pastures. Visited on 6 and 7 December 2002. The general region presents a mosaic of habitats, ranging from open pastures and agricultural fields, to cerrado, cerraddo, areas with an influence of open (usually degraded) caatinga, arboreal caatinga, ‘mata de Jaiba’, deciduous and semi-deciduous forests, strips of gallery woodland, and some remaining patches of tall woodland (where ‘jatoba’ Hymenaea sp. abounds). This mix of habitats is a result of the geographical location of this area, at the meeting points of the cerrado and caatinga biomes, and several areas represent transitional habitats (Rizzini 1997). Natural habitats have been greatly modified by human actions, and currently only a few areas of intact woodlands remain, where once rich forests existed (Hartt 1870, Spix & Martius 1981). These forests have been felled mainly to provide open Guy M. Kirwan et al. 210 Bull. B.O.C. 2004 124(3) land for agriculture, Eucalyptus plantations, and to produce carbon, an activity noted at Fazendas Jatoba do Cotobelo and Jatoba da Mata. Silva & Oren (1992, 1997) alerted ornithologists to the fragile situation of the remaining deciduous forests growing on calcareous soils, and Kirwan et al. (2001) and Raposo et al. (2002) added further details concerning habitat modification in the region. We suggest that imminent land-use reform will be required if remaining natural habitats are to be sustainably managed. We also checked specimens collected in the region housed in two Brazilian collections: the ‘Colegao Ornitologica do Departamento de Zoologia da Universidade Federal de Minas Gerais’ (DZUFMG) in Belo Horizonte, Minas Gerais; and the ‘Museu de Historia Natural de Taubaté’ (MHNT), in Taubaté, Sao Paulo. Species accounts MISSISSIPPI KITE /ctinia mississippiensis Three observed soaring over Fazenda Jatoba da Mata, south of Varzea da Palma, on 10 January 2003 (IR) is about the sixth country record. All individuals had unbarred tails, a diagnostic character to distinguish this species from Plumbeous Kite J. plumbea, with which IR is very familiar. First recorded in Brazil, at the Anavilhanas archipelago, Amazonas, in late November 1985 (Stotz et al. 1992) with subsequent sight records of migrant flocks in Mato Grosso: 82 over Chapada dos Guimaraes on 14 November 1996 (A. Whittaker in Mazar Barnett et al. 1999), over 200 south of Poconé on 17 October 1997 (H. Buck in Mazar Barnett & Kirwan 2000a), c.20 between Poconé and the rio Pixiam on 12 October 1999 and 63 at the Chapada dos Guimaraes on 14 October 1999 (P. O’Neill in Mazar Barnett & Kirwan 2000b).° Wintering range very imprecisely known. The largest numbers are postulated to be in Paraguay, although Hayes (1995) considered it to be rare in most regions of the country, and northern Argentina (del Hoyo et al. 1994). Speculated also to winter in adjacent south-east Bolivia and south-west Brazil (Ferguson-Lees & Christie 2001). The present record seems to indicate that, at least in small numbers, the species does, indeed, winter in Brazil. ORNATE HAWK-EAGLE Spizaetus ornatus Singles observed at Parque Nacional Cavernas do Peruagu on 30 May and 24 August 2002 (MFV, SDN). On both occasions, they were flying over patches of arboreal caatinga on limestone outcrops, and the latter was tape-recorded. Ornate Hawk-eagle is a threatened species in Minas Gerais (Lins et al. 1997) and this is the first state record from within a protected area (Brandt 1998). WHITE-BROWED GUAN Penelope jacucaca A specimen was taken, by S. F. Guimaraes, at Jatoba (15°18’S, 44°10’W), Januaria municipality, on 21 August 2000 (MHNT 4561). This becomes the second state Guy M. Kirwan et al. 211 Bull. B.O.C. 2004 124(3) locality, after Mocambinho (Kirwan ef a/. 2001), from where a specimen is also available, taken by J. E. Simon and J. M. C. da Silva on 29 July 1998 (DZUFMG 2883). LEAST NIGHTHAWK Chordeiles pusillus Up to 50 observed over the rio das Velhas, south of Pirapora, on | and 21 October 2002 (GMK, MAE, GMF, RS ef a/.), with fewer individuals noted in early-January 2003 at Rio Lavado and west of Lassance. We had not previously recorded the species in this region (Kirwan ef a/. 2001) and Willis & Oniki (1991) did not record it at Januaria. We use these observations to draw attention to the fact, overlooked by Cleere & Nurney (1998) and Cleere (1999), that races other than northerly esmeral- dae also undertake seasonal movements. Holyoak (2001) also provided very little information on such migrations. We have observed this species in several areas of Sao Paulo, e.g. around Itirapina, and Minas Gerais states, e.g. at the Serra do Cipo, Serra da Canastra and elsewhere, on a distinctly seasonal basis, confirming that nominate pusillus also makes regular migratory movements, as mentioned by Sick (1997). The recent discovery that this species breeds in north-eastern Argentina (Krauczuk 1998), and the timing of records there, also indicate migrations. PLAIN-TAILED NIGHTHAWK WNyctiprogne vielliardi Until recently known only from the type locality in Bahia, near Manga (Lencioni- Neto 1994), but its known range was thereafter extended south to central Minas Gerais, in the proximity of Pirapora (Whitney et a/. 2003). In previous visits to the region GMK, JMB ef a/. witnessed large concentrations of these nighthawks along the Sao Francisco and its main tributaries, considering them to be common in areas around Pirapora, Januéria and Mocambinho. At the last we noted groups of 150—200 individuals subdivided into smaller flocks (Whitney et al. 2003). Remarkably, during our October and November 2002 and January 2003 visits to the same area, it was only with considerable difficulty that we located any N. vielliardi, with none at Mocambinho, very few south of Pirapora, on 12 October (GMK et al.), and only two individuals 10 km south of Januaria, on 13 January (GMK, JMB, IR). Searches for the species at other, apparently suitable areas of the rio Sao Francisco, e.g. immediately south-west of the town of Pirapora, in February 2002 (GMK, DB, AG, JM) failed to locate any N. vielliardi. The reasons for this drastic variation in numbers can only be speculated. Seasonal movements are plausible, but our mid- December 1999 and mid-January 2003 visits differed in timing by as little as three weeks, and it appears unlikely that the species engages in such migrations (seasonal movements in Band-tailed Nighthawk N. /eucopyga are known from only one small area of Brazil and nowhere else across its broad range; Holyoak 2001). Climatic events are not likely to have played a major role, nor has habitat modification of those areas used by this species been documented in the region, to the extent to which it would have caused such results. Originally described in Chordeiles, Guy M. Kirwan et al. 22 Bull. B.O.C. 2004 124(3) Whitney et al. (2003) provided detailed rationale for considering it within Nyctiprogne. PYGMY NIGHTJAR Caprimulgus hirundinaceus During nocturnal surveys, a female was spotlighted down to distances of just 25 cm, 12 km south of Pirapora, on | October 2002 (GMK, RS et al.). Its very small size was immediately apparent, and contrasted noticeably with the other caprimulgids present on the same dirt road, Pauraque Nyctidromus albicollis and Scissor-tailed Nightjar Hydropsalis torquata. It had only restricted white in the primaries and lacked any white in the tail. Little Nightjar C. parvulus might be expected at this season in this part of Minas Gerais (Sick 1997, Melo et al. 2000), although we have failed to record it at any localities in this region (Kirwan et al. 2001), but was eliminated because it possesses a broad hindneck collar, more extensive white throat, more broadly patterned wing-coverts, supercilium effect, and lacks any white in the wing. Given the very dark plumage of the form C. h. vielliardi, which may even lead observers to mistake it for Blackish Nightjar C. nigrescens (Ribon 2000), we attribute this record to the nominate subspecies, the first locality in Minas Gerais. Three races of this Brazilian endemic are currently recognised: the nominate in the arid north-east from southern Piaui to Bahia and Alagoas, C. h. cearae from northern Ceara to extreme northern Bahia and the recently described C. h. vielliardi from one locality in Espirito Santo and another in extreme eastern Minas Gerais (Ribon 1995, Cleere & Nurney 1998, Vasconcelos & Lins 1998). FRILLED COQUETTE Lophornis magnificus A male observed periodically over 30 minutes within a patch of tall woodland on the left bank of the rio Sao Francisco, 15 km south of Januaria, on 10 February 2002 (DB, AG, GMK, JM) and another male in the same area on 15 January 2003 (GMK). Occurs principally in east coastal Brazil, from Alagoas south to Rio Grande do Sul, and west to Goias and Mato Grosso (Sick 1997, del Hoyo et al. 1999), but there appear to be few, if any, previous mentions of the species for Minas Gerais. SILVERY-CHEEKED ANTSHRIKE Sakesphorus cristatus Only recently discovered to be relatively widespread in the middle reaches of Sao Francisco Valley in the extreme south-west of its range (Kirwan ef al. 2001). Four specimens deposited in DZUFMG were taken at Mocambinho between 14 and 18 September 1996 by G. T. Mattos (DZUFMG 2521, DZUFMG 2522, DZUFMG 2523, DZUFMG 2524; two males and two females). Additional sight-record locali- ties are: Japoré, Poco da Vovo region, and Fazenda Nova Uniao, (MFV, SDN), and, extending the species’ range further south from Pirapora (Kirwan et al. 2001), just west of Varzea da Palma on 10 January 2003 (GMK). Guy M. Kirwan et al. 213 Bull. B.O.C. 2004 124(3) CHOTOY SPINETAIL Schoeniophylax phryganophilus This relatively common and widespread species of light woodland and scrubland of south-central South America has an isolated population (petersi) in the middle reaches of the Sao Francisco valley. Pinto (1978) only mentioned it for Pirapora, in Minas Gerais, and Barra in Bahia. Sick (1997), probably assuming a continuous distribution, considered it to occur in the Sao Francisco Valley of interior Bahia and Minas Gerais. We have recorded this taxon at a number of localities in the study region, and though they are all broadly within its known range, very little has been published concerning this form’s distribution. Specific Minas Gerais localities from the literature, other than Pirapora (Pinto 1978, Kirwan ef al. 2001) are near Itacarambi (Kirwan ef al. 2001), and south of Januaria (Willis & Oniki 1991). We have also recorded the species c.10 km north of Januaria, on 14 January 2003, and between Varzea da Palma and Lassance, on 10 January 2003, when a pair was found nest-building, taking material from a disused Common (Rufous-fronted) Thornbird Phacellodomus rufifrons nest. This would appear to be the southernmost record for petersi. In addition, a female specimen (DZUFMG 2489) was taken by G. T. Mattos at Mocambinho on 23 November 1996, and MFV has collected others on the western slope of the Serra do Espinhaco in recent years. The species is almost certainly frequent in woodland edge, degraded brush and agricultural land through- out north-central and extreme north-east Minas Gerais. The validity of petersi is perhaps questionable (e.g. Vaurie 1980, Brammer 2002, MFV pers. obs.), although a thorough analysis, including vocalisations, is still lacking. RED-SHOULDERED SPINETAIL Gyalophylax hellmayri Observed at Japoré, on 6 July 2002 (SDN), where one vocalised close to the ground in secondary low caatinga. This is only the third published state locality for G. hellmayri, which is considered globally Near Threatened (BirdLife International 2000). GREATER WAGTAIL-TYRANT Stigmatura budytoides The form S. b. gracilis appeared to be rather common in scrub on the left bank of the rio Sao Francisco, 15 km south of Januaria, on 10 February 2002 (DB, AG, GMK, JM; tape-recorded) and 13 January 2003 (GMK). The species was first reported for Minas Gerais by Kirwan et al. (2001) from Mocambinho, where further observations by DB, AG, JM and ourselves have demonstrated it to be common. The new locality extends its range further south by c.70 km. We will comment elsewhere on the taxonomy of this genus. MINAS GERAIS TYRANNULET Phylloscartes roquettei Raposo ef al. (2002) presented details of observations from two localities in the rio Sao Francisco Valley. At one of these, the Corrego dos Ovos, GMK, RS et al. subsequently discovered a pair (the subject of comparatively regular observation in recent years) nest-building on 1—2 October 2002. The nest was located c.10 m above Guy M. Kirwan et al. 214 Bull. B.O.C. 2004 124(3) ground in a tree flanking the corrego (stream) and situated within | m of a termitar- ium suspended close to the main trunk. The nest was broadly globular in shape, slightly distended top to bottom (as is typical among several genera of tyrannid flycatchers) with a short side entrance tube, and was constructed of fine rootlets, dead twigs, lichens, grassy material and a small number of dead leaves, and without an inner chamber at this stage (visible because the nest was sufficiently ‘transpar- ent’). It was attached to a small branch, almost at its extreme tip, and its approximate dimensions were 10 cm in height and 6—7 cm across. The pair was actively collecting nest material, usually very close to or from the ground, when they appeared almost fearless and would perch within very close proximity of the observers (photographed; see Fig. 2). GMK (together with MAE, GMF et al.) returned to the area on 21—22 October 2002, by which time the nest had apparently been completed (Fig. 3). Only one individual was seen throughout the 2—3-hour observation period, and the other was presumed to be sitting. A further visit to the area, on 11 January 2003, revealed no sign of the pair, despite use of playback (they are usually exceptionally responsive) or even the nest. These data are the first available concerning this species’ breeding biology. Elsewhere in January 2003, JMB, GMK, IR and HS conducted further playback surveys for the species at several apparently suitable localities in the general region, at Fazenda Jatoba da Mata, along the road through the Companhia Florestal, south of Pirapora, along the road to Serra do Boqueirao and near Jequitai, near Brejo do Amparo, along the Sao Francisco river south of Januaria, and north of Januaria, also without success. Subsequently, however, it has been found in the Cavernas do Peruacgu National Park, by Dante Buzzetti (see del Hoyo ef al. in press). We can only assume that P roquet- Figure 2. Minas Gerais Tyrannulet Phylloscartes roquettei, south of Pirapora, Minas Gerais (Rick Schaefer) Figure 3. Nest of Minas Gerais Tyrannulet Phylloscartes roquettei, south of Pirapora, Minas Gerais (Louise Augustine) Guy M. Kirwan et al. 215 Bull. B.O.C. 2004 124(3) tei is genuinely rather uncommon within its apparently limited range, presumably to large extent due to the ongoing logging of tall emergent trees in this area of Brazil. STRIPE-NECKED TODY-TYRANT Hemitriccus striaticollis Regularly observed in small numbers 12 km south of Pirapora in degraded gallery forest fringing the rio das Velhas (GMK ef al.; Kirwan et al. 2001). One was observed in second growth of gallery forest at the left margin of the rio Sao Francisco on 27 April 2002, near Riacho da Cruz village. It vocalised while foraging in the understorey (MFV, SDN). Another was tape-recorded in riverine scrub along the road to Mocambinho, on the right bank of the rio Sao Francisco, on 12 January 2003 (JMB), and two pairs were tape-recorded in similar habitat, but on the left bank of this river, c.15 km south of Januaria, on 13 January 2003 (JMB, IR). These individuals moved within the tangled understorey of riverine woodland. This is a little-known species in Minas Gerais and the records south of Pirapora appear to represent the southernmost state locality for the species (see map in Ridgely & Tudor 1994). Although the species was known from this area, its regional distribu- tion is poorly documented, and our records serve to underscore the fact that it is relatively widespread, where suitable habitat exists. CAATINGA BLACK-TYRANT Knipolegus franciscanus MFYV and SDN observed K. franciscanus at Parque Nacional Cavernas do Peruacu, on 30-31 May and 24-25 August 2002, confirming previous observations by Andrade (1990). A single male was observed on both occasions, and was photographed. It perched close to an arboreal caatinga edge near a limestone outcrop. On 14 January 2003, GMK, JMB and IR observed a lone male in low- stature dry forest atop a relatively low rocky outcrop (/ajeiro) between Riacho da Cruz and Levinopolis, on the left bank of the Sao Francisco. This was the only individual found between Pirapora and Itacarambi in four days of searching throughout the area. Notably, it was discovered near human habitation. As is usual in our experience of this form, it behaved rather unobtrusively, unlike many others within the genus Knipolegus, perching quietly and occasionally very low within the low crowns of the open forest, and only intermittently conducting short, low foraging sallies. Sometimes perched on more exposed situations such as a dead cactus, hanging branches or even on top of rocks. Sally flights were normally within the crown of small trees and also towards the ground. It delivered short, nervous tail flicks. We believe that this species’ rather unobtrusive behaviour renders it difficult to find in the taller, more densely vegetated sandstone outcrops that abound in the region. It is therefore probably commoner in the area than our records suggest, although the species clearly has a rather restricted range and specific habitat requirements, and is evidently not common. One exception to this is an area known as Curral de Pedras (17°06’S, 44°35’W), where as many 50 individuals were seen in just one hour, on 22 November 1995 (MAR). Three males and a female were Guy M. Kirwan et al. 216 Bull. B.O.C. 2004 124(3) collected and are housed at the Museu Nacional do Rio de Janeiro (MNRJ 42730/3 1/32/33). Lima (1999) listed only five localities (including Jequitai) in Minas Gerais for this highly localised and only recently recognised species (Silva & Oren 1992). LONG-BILLED WREN Thryothorus longirostris One (tape-recorded and photographed) responded weakly and with an unfamiliar vocalisation to playback of the voice of T /. bahiae, at Mocambinho, on 9 February 2002 (DB, AG, GMK, JM) and several of this form were found in caatinga at Parque Nacional Cavernas do Peruacu, on 30-31 May 2002 (MFV, SDN) and 13 January 2003 (JMB, IR, HS; when tape-recorded). MFV and SDN also found the species on the right bank of the Sao Francisco, in the Pogo da Vovo region, on 7 July 2002. In addition, two specimen records are available for the state, both held at DZUFMG and taken at Mocambinho: DZUFMG 2572 (male) taken on 4 April 1997 by M. R. Bornschein, B. L. Reinert and M. M. Coelho, and DZUFMG 2529 (female) taken on 20 May 1997 by G. T. Mattos. These specimens were compared to the nominate race and appear to belong to 7 /. bahiae. They also appear to be the first state records, but are unsurprising given the discovery of several other caatinga species from further north in this area of Minas Gerais in recent years. Indeed, MFV and SDN have found this form to be very common in the caatinga of much of northern Minas Gerais, including away from the Sao Francisco Valley. Specimens have been deposited at DZUFMG. Brewer & MacKay (2002) considered the range of 7. 1. bahiae to encompass Ceara and eastern Piaui south to northern Bahia and Alagoas. We will comment elsewhere on the taxonomy of this species. SCARLET-THROATED TANAGER Compsothraupis loricata Found at two new localities in January 2003 (GMK, JMB, IR), at Rio Lavado and along the road through the Companhia Florestal, up to 75 km south of Pirapora, which is the southernmost locality for this Brazilian endemic mentioned by Sick (1997). It was also recorded at a number of sites around Pirapora and further north. The species seems relatively abundant in the southernmost edge of its range, and is normally encountered in flocks of 5—15 individuals (possibly involving family groups), mostly in gallery woodlands and taller wooded areas. GREY-HEADED TANAGER Eucometis penicillata One observed at close quarters in patchy forest bordering the left bank of the rio Sao Francisco, 10 km south of Januaria, on 10 February 2002 (DB, AG, GMK, JM). This widespread species reaches its farthest south and east in Goias, and western Sao Paulo and Minas Gerais states (Sick 1997). Our record extends its range to north-central Minas Gerais, a distance of c.170 km from one of the closest specific localities that we can locate, Parque Nacional de Brasilia (Forrester 1993). Guy M. Kirwan et al. 217 Bull. B.O.C. 2004 124(3) RUSTY-COLLARED SEEDEATER Sporophila collaris Three males were present at the scrubby edges of an extensive marsh beside the road between Jequitai and the Serra do Boqueirao, on 11 January 2003 (GMK, JMB, IR, HS). They were observed feeding in the open rush-beds fringing the waterbody, and flying back and forth between there and scrubby marsh away from the open waterside. No female-plumaged individuals were found. In the field these birds appeared uniform black from the crown, forehead and cheeks to the lower mantle, with an obvious pale grey rump, the tail and wings were black, with a white speculum, and a white bar on the median wing-coverts. The white throat extended as a half-collar below the cheeks and onto the ear-coverts, but did not meet on the hindneck. There was a broad black pectoral band and otherwise white underparts. Previously, MAR had collected a male probably at the same marsh as the observa- tions above, in 1995 (MNRJ 42726), and a second specimen (MNRJ 28817) from Concei¢ao da Aparecida, south of Belo Horizonte, Minas Gerais, with slightly more ochre suffusion on the belly, was found among the S. americana specimens in that institution. These specimens are very different to all other S. collaris examined by us in MNRJ but they do recall one, of uncertain locality in Brazil, in the Natural History Museum (Tring, accession number 85.2.10.132). They are, in many respects, closer to S. americana than to other S. collaris due to the predominantly black-and-white plumage, partial nuchal collar, greyer rump and black pectoral band, although the last was broader than in typical americana and unbroken, and there was no trace of a greater covert bar. JMB considered that the bill morphology of these Minas Gerais specimens was strikingly similar to that of specimens of S. americana from northern Amazonia housed at MNRJ, and quite different from S. collaris specimens in the same institution. Sharing morphological and plumage characters with both S. americana and S. collaris, we feel unsure as to the taxonomic identity of this population. This also opens questions concerning previous southern records of S. americana (e.g. Stuart 2000). Subspecies limits within S. collaris are currently under review by MAR, as more than one species may be involved. SAO FRANCISCO SPARROW 4rremon franciscanus Our observations in the newly declared Parque Nacional Cavernas do Peruacu indicate this recently described and globally Near-Threatened species (BirdLife International 2000) to be rather common there. We have also discovered it in the Pogo da Vovo region, on 7 July 2002 (MFV, SDN) and in scrubby, heavily degraded roadside caatinga just north of Montalvania, on 8 February 2002 (DB, AG, GMK, JM). An additional specimen (the sixth) to those mentioned by Raposo (1997) is available: a male taken at Mocambinho by G. T. Mattos on 19 May 1997 (DZUFMG 2480). Further south, e.g. around Pirapora, the species appears to be replaced by Saffron-billed Sparrow A. flavirostris, which until recently was known from rather few localities in the state (Raposo 1997) principally in the west (e.g. Sick 1997, Silveira 1998, Marini 2001) but also to the centre, around Belo Horizonte (Melo- Guy M. Kirwan et al. 218 Bull. B.O.C. 2004 124(3) Junior et al. 2001, Vasconcelos & Melo-Junior 2001; GMK pers. obs.), and south (Vasconcelos et al. 2002). Thus far, A. franciscanus appears to be known from just eight, perhaps nine localities (Raposo 1997, Parrini et al. 1999, Kirwan et al. 2001, D’ Angelo Neto & Vasconcelos unpubl.), though we suspect that it is reasonably common in suitable habitat within its comparatively small range. A record of A. flavirostris from Manga (Mattos eft al. 1991) may well be in error, as A. francis- canus was undescribed at that time, and the latter seems much more likely to occur at this site (J. F Pacheco in Jitt. 2003). FORBES’S BLACKBIRD Curaeus forbesi It appears worthy of remark that we have searched for this globally threatened species at several localities in the region, without success, notably at the sugarcane fields and marshy areas fringed by woodlands at Brejo do Amparo (JMB, GMK, IR), where probably observed in 1977 by Willis & Oniki (1991) and south of Pirapora, at the rio das Velhas, where found by E. Willis and H. Remold in 1999 (BirdLife International 2000). The habitat at the former is similar to that where the species 1s known from in Pernambuco (JMB, IR pers. obs, L. A. P. Gonzaga and W. Silva pers. comm.). Acknowledgements Among others, the following observers, indicated by their initials in the text, jomed GMK and JMB in recent field trips to the middle reaches of the rio Sao Francisco Valley: Dave Beadle (DB), Mark Elwonger (MAE), Mike Flieg (GMF), Arthur Grosset (AG), Jeremy Minns (JM), Rick Schaefer (RS) and Hadoram Shirihai (HS). GMK is grateful to Robert Prys-Jones and Mark Adams at the Natural History Museum (Tring) for access to specimen material at that institution. J. A. Silva kindly prepared the map. Chris Feare, the editor, and Fernando Pacheco, as referee, made several comments which improved the manuscript. References: Andrade, M. A. 1990. Importancia ornitolo6gica do vale do Peruagu. O Charao 16: 18. BirdLife International 2000. Threatened birds of the world. BirdLife International, Cambridge, UK & Lynx Edicions, Barcelona. Brammer, F. 2002. Species concepts and conservation priorities: a study of birds in north-east Brazil. M.Sc. thesis. Zool. Mus., Univ. Copenhagen, Denmark. Brandt, L. F. S. 1998. Spizaetus ornatus (Daudin, 1800). Pp. 211—213 in Machado, A. B. M., Fonseca, G. A. B., Machado, R. B., Aguiar, L. M. S. & Lins, L. V. (eds.). Livro vermelho das espécies ameagadas de extingado da fauna de Minas Gerais. Fundagao Biodiversitas, Belo Horizonte. Brewer, D. & MacKay, B. K. 2002. Wrens, dippers and thrashers. Christopher Helm, London. Cleere, N. 1999. Family Caprimulgidae (nightjars). Pp. 302-386 in del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) Handbook of the birds of the world, vol. 5. Lynx Edicions, Sangean Cleere, N. & Nurney, D. 1998. Nightjars: a guide to nightjars and related nightbirds. Pies Press, Robertsbridge. Ferguson-Lees, J. & Christie, D. A. 2001. Raptors of the world. Christopher Helm, London. Forrester, B. C. 1993. Birding Brazil: a check-list and site guide. Privately published, Irvine. Hartt, C. F 1870. Geology and physical geography of Brazil. Jn Agassiz, L. (ed.) Scientific results of a Journey in Brazil. Fields, Osgood & Co, Boston. Hayes, F. E. 1995. Status, distribution and biogeography of the birds of Paraguay. Monogr. Field Orn. 1. American Birding Association, Colorado Springs. Guy M. Kirwan et al. 219 Bull. B.O.C. 2004 124(3) Holyoak, D. T. 2001. Nightjars and their allies. Oxford Univ. Press. del Hoyo, J., Elliott, A. & Christie, D. (eds.) in press. Handbook of the birds of the world, vol. 9. Lynx Edicions, Barcelona. del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 1994. Handbook of the birds of the world, vol. 2. Lynx Edicions, Barcelona. del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) 1999. Handbook of the birds of the world, vol. 5. Lynx Edicions, Barcelona. Kirwan, G. M., Mazar Barnett, J. & Minns, J. 2001. Significant ornithological observations from the Rio Sao Francisco Valley, Minas Gerais, Brazil, with notes on conservation and biogeography. Ararajuba 9: 145-161. Krauczuk, E. R. 1998. Estudio cuantitativo de aves de pajonal en Campo San Juan, Misiones, Argentina. P. 148 in Resumos VII Congresso Brasileiro de Ornitologia (Rio de Janeiro, July 1998). Lencioni-Neto, F. 1994. Une nouvelle espece de Chordeiles (Aves, Caprimulgidae) de Bahia (Brésil). Alauda 62: 242-245. Lima, F. C. T. de 1999. A range extension for the Caatinga Black-tyrant, Knipolegus franciscanus (Tyrannidae), a rare Brazilian endemic. Bull. Brit. Orn. Cl. 119: 270-271. Lins, L. V., Machado, A. B. M., Costa, C. M. R. & Herrmann, G. 1997. Roteiro metodoldgico para elab- oracgao de listas de espécies ameagadas de extingao: (contendo a lista oficial da fauna ameagada de extincao de Minas Gerais). Publ. Av. Fund. Biodiversitas 1: 1—S0. Marini, M. A. 2001. Effects of forest fragmentation on birds of the cerrado region, Brazil. Bird Conserv. Intern. 11: 13-25. Mattos, G. T., Andrade, M. A. & Freitas, M. V. 1991. Levantamento de aves silvestres na regiao noroeste de Minas Gerais. Rev. SOM 39: 26-29. Mazar Barnett, J. & Kirwan, G. M. (compilers) 2000a. Neotropical notebook: Brazil. Cotinga 13: 75. Mazar Barnett, J. & Kirwan, G. M. (compilers) 2000b. Neotropical notebook: Brazil. Cotinga 14: 106. Mazar Barnett, J., Kirwan, G. M. & Tobias, J. (compilers) 1999. Neotropical notebook: Brazil. Cotinga 11: 101. Melo, L. A. C. de, Faria, L. P., Vasconcelos, M. F. & Rodrigues, M. 2000. Nidificagao e cuidado parental do bacurau-pequeno, Caprimulgus parvulus Gould, 1837, no Parque Nacional da Serra do Cipo, Minas Gerais. Ararajuba 8: 109-113. Melo-Junior, T. A., Vasconcelos, M. F., Fernandes, G. W. & Marini, M. A. 2001. Bird species distribu- tion and conservation in Serra do Cipo, Minas Gerais, Brazil. Bird Conserv. Intern. 11: 189-204. Parrini, R., Raposo, M. A., Pacheco, J. EF, Carvalhaes, A. M. P., Melo-Junior, T. A., Fonseca, P. S. M. da & Minns, J. 1999. Birds of the Chapada Diamantina, Bahia, Brazil. Cotinga 11: 86-95. Pinto, O. M. O. 1978. Novo catalogo das aves do Brasil. Primeira parte. Empresa Grafica da Revista dos Tribunais, Sao Paulo. Raposo, M. A. 1997. A new species of Arremon (Passeriformes: Emberizidae) from Brazil. Ararajuba 5: 3-9. Raposo, M. A., Mazar Barnett, J., Kirwan, G. M. & Parrini, R. 2002. New data concerning the distribu- tion, behaviour, ecology and taxonomic relationships of Minas Gerais Tyrannulet Phylloscartes roquettei. Bird Conserv. Intern. 12: 241-253. Ribon, R. 1995. Nova subspécie de Caprimulgus (Linnaeus) (Aves, Caprimulgidae) do Espirito Santo, Brasil. Rev. Bras. Zool. 12: 333-337. Ribon, R. 2000. Até prova em contrario nao ha Caprimulgus nigrescens no sudeste do Brasil. E nem Xiphocolaptes falcirostris franciscanus na margem direita do rio Sao Francisco. Bol. Soc. Bras. Ornitologia, Sao Paulo 30: 8-9. Ridgely, R. S. & Tudor, G. 1994. The birds of South America, vol. 2. Univ. Texas Press, Austin. Rizzini, C. T. 1997. Tratado de fitogeografia do Brasil: aspectos ecologicos, sociologicos e floristicos. Ambito Cultural Edicdes, Rio de Janeiro. Sick, H. 1997. Ornitologia brasileira. Ed. Nova Fronteira, Rio de Janeiro. Silva, J. M. C. da & Oren, D. C. 1992. Notes on Knipolegus franciscanus Snethlage, 1928 (Aves: Tyrannidae), an endemism of central dry Brazilian forests. Goeldiana Zool. 16: \—9. Guy M. Kirwan et al. 220 Bull. B.O.C. 2004 124(3) Silva, J. M. C. da & Oren, D. C. 1997. Geographic variation and conservation of the Moustached Woodcreeper Xiphocolaptes falcirostris, an endemic and threatened species of north-eastern Brazil. Bird Conserv. Intern. 7: 263-274. Silveira, L. F 1998. The birds of Serra da Canastra National Park and adjacent areas, Minas Gerais, Brazil. Cotinga 10: 55-63. Snethlage, E. 1928. Novas especies e subspecies de aves do Brasil Central. Bol. Mus. Nac. 4: 1-7. Spix, J. B. & Martius, C. F. P. 1981. Viagem pelo Brasil: 1817-1820, vol. 2. Sao Paulo & Belo Horizonte, Ed. Universidade de Sao Paulo & Ed. Itatiaia. Stotz, D. F., Bierregaard, R. O., Cohn-Haft, M., Petermann, P., Smith, J., Whittaker, A. & Wilson, S. V. 1992. The status of North American migrants in central Amazonian Brazil. Condor 94: 608-621. Stuart, T. E. H. 2000. The first record of Variable Seedeater Sporophila americana in Bolivia. Cotinga 182376. Vasconcelos, M. F. & Lins, L. V. 1998. First records of Caprimulgus hirundinaceus vielliardi for Minas Gerais state, Brazil. Ararajuba 6: 134-135. Vasconcelos, M. F & Melo-Junior, T. A. 2001. An ornithological survey of Serra do Caraga, Minas Gerais, Brazil. Cotinga 15: 21-31. Vasconcelos, M. F., D’Angelo-Neto, S., Brandt, L. F S, Venturin, N., Oliveira-Filho, A. T. & Costa, F. A. F. 2002. Avifauna de Lavras e municipios adjacentes, Sul de Minas Gerais, e comentarios sobre sua conservac¢gao. Unimontes Cientifica 4: 153-165. Vaurie, C. 1980. Taxonomy and geographical distribution of the Furnariidae (Aves, Passeriformes). Bull. Amer. Mus. Nat. Hist. 166: 1-357. Whitney, B. M., Pacheco, J. FE, Fonseca, P. S. M., Webster, R. E., Kirwan, G. M. & Mazar Barnett, J. 2003. Reassignment of Chordeiles vielliardi Lencioni-Neto, 1994, to Nyctiprogne Bonaparte, 1854, with comments on the latter genus and some presumably related chordeilines (Aves: Caprimulgidae). Bull. Brit. Orn. Cl. 123: 103-112. Willis, E. O. & Oniki, Y. 1991. Avifaunal transects across the open zones of northern Minas Gerais, Brazil. Ararajuba 2: 41-58. Addresses: Guy M. Kirwan, 74 Waddington Street, Norwich NR2 4JS, UK. Juan Mazar Barnett, Av. Forest 1531 1°B, (1430) Buenos Aires, Argentina. Marcelo Ferreira de Vasconcelos, Departamento de Biologia Geral, Universidade Estadual de Montes Claros, Av. Rui Braga, s/ne 39401-089, Montes Claros, Minas Gerais, Brazil. Marcos A. Raposo, Setor de Aves, Departamento de Vertebrados, Museu Nacional, Quinta da Boa Vista, s/ne Rio de Janeiro, RJ 20940-040, Brazil. Santos D’Angelo Neto, Departamento de Biologia Geral, Universidade Estadual de Montes Claros, Av. Rui Braga, s/ne 39401-089, Montes Claros, Minas Gerais, Brazil. Ignacio Roesler, Calle 2 N°1187, (1900) La Plata, Buenos Aires, Argentina. © British Ornithologists’ Club 2004 AN | MOV tis /, MEMBERSHIP See also website: http://www.boc-online.org Subscription rates for 2004 were due for renewal on | January 2004 but will increase on | January 2005 2004 2005 BOU Members £12.00 (US $24.00) £17.50 (US $36.00) Non-BOU Members £18.00 (US $34.00) £24.00 (US $48.00) All paid-up Members of the Club receive (postage free) four quarterly issues of the Bulletin, and the annual index. New Members are welcomed, at any time. CORRESPONDENCE Correspondence on all general Club matters should be addressed to: The Hon. Secretary, S.A.H. (Tony) Statham, Woodcock Hill, Durrants Lane, Berkhamsted, Herts. HP4 3TR, UK (or e-mail: SAHS@tinyon- line.co.uk). For details of Club Meetings see inside front cover. Correspondence and applications for membership, and changes of address should be addressed to: The Membership Secretary, Cdr. M.B. Casement, OBE, RN, Dene Cottage, West Harting, Petersfield, Hants. GU31 5PA, UK (or e-mail: mbcasement@aol.com). The Membership List 2004 is available, free of charge, on application to the Membership Secretary. This shows addresses (including e-mail addresses, where known), for all paid-up Members as at 31 December 2003. Members are requested to inform him of all corrections or changes, without delay, for dispatch of the Bulletin. To offset the cost of postage, any contribution, or a stamped and addressed (A5-sized) envelope will be gratefully accepted. 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Publications Officer BOC, Natural Resources Institute, University of Greenwich at Medway, Central Avenue, Chatham Maritime, Chatham, Kent ME4 4TB (e-mail: r.a.cheke@greenwich.ac.uk) PAYMENTS All amounts quoted are net and should be paid in £ sterling, if possible. Payments in other currencies must include a further £4 for UK bank charges (except for annual rates in US dollars, which are inclusive). All cheques or drafts should be made payable to the British Ornithologists’ Club. If preferred, remittances may be made by bank transfer direct to the Club’s bank account: Barclays Prime Account, Dale House, Wavertree Boulevard, Liverpool L7 9PQ, UK. (Sort Code 20-00-87 Account No. 10211540), with confirmation to the Hon. Treasurer, D.J. Montier, Eyebrook, Oldfield Road, Bickley, Bromley, Kent BR1 2LF. COMMITTEE Dr C.F. Mann (Chairman) (2001) I.R. Bishop OBE (2003) Mrs M.N. Muller (Vice-Chairman) (2003) eZ C.W.R. Storey (2003) S.A.H. Statham (Hon. Secretary) (2004) ae J.P. Hume (2004) D.J. Montier (Hon. Treasurer) (1997) Dr P.G.W. Salaman (Hon. Website Manager) (2001) Prof. R.A. Cheke (BOC Publications) (2001) Ex-officio members Hon. Editor: G.M. Kirwan (1 January 2004) Chairman of BOU/BOC Joint Publications Committee (JPC): Reverend T.W. Gladwin. Membership Secretary: Cdr. M.B. Casement OBE RN (2004) Registered Charity No. 279583 Pe “ulletin of the British Ornithologists’ Club ISSN 0007-1 595 _ Edited by Guy M. Kirw: — 124, Number 3, pages 157-220 INSTITUTION LIBRARIES wii Nt Ml CONTENTS Club Announcements 2.6605 ae vo wks ba kw Rs 2 ee lee INDRAWAN, M. & SOMADIKARTA, S. A new hawk-owl from the Togian Isla Tomini, central Sulawesi, Indonesia... .. 30.005 24. ons ca Pa: LOWTHER, P. E., FRAGA, R., SCHULENBERG, T. S. & LANYON, S. M. Nome colulien Rar a paleuieiciay Actas eb adludw eam hake pore 6 op 6 6 bate ele RODRIGUES, M. & BELFORT GOMES, H. Range extension for Greyiusgiell Tanag Eucometis penicillata in south-east Brazil... ..........04..+s00.+122)55 eigen BRUCE, M. D. & DOWSETT, R. J. The correct name of the Afrotropical mainland subspecies of — | Barn Owl Tyto alba ... 2. oe ens cen cea ee wen ee , FREILE, J. F Range extensions and other noteworthy and new bird records from mainland © Bee@adOr 2. ois oi ea be ea va cles en te ee ok « aye 6 ay ea BRIED, J. & MAGALHAES, M. C. First Palearctic record of the endangered Bermuda Petrel Pterodroma cahow .. o.oo ccc a cee ce ewe sae we ce sen dad say eee KIRWAN, G. M., MAZAR BARNETT, J., VASCONCELOS, M. FE. RAPOSO, M. A., DDANGELO NETO, S. & ROESLER, I. Further comments on the avifauna of the middle Sao Francisco Valley, Minas Gerais, Brazil .. 2... 0.30605 nee ae ee ese so er Authors are invited to submit papers on topics relating to the broad themes of taxonomy and distribution of birds. Descriptions of new species of birds are especially welcome and will be given priority to ensure rapid publication, subject to successful passage through the normal peer review procedure, and they may be © accompanied by colour photographs or paintings. On submission, manuscripts, double-spaced and with wide margins, should be sent to the Editor, Guy Kirwan, preferably by e-mail, to GMKirwan@aol.com. Alternatively, two copies of manuscripts, typed on one side of the paper, may be submitted to the Editor, 74 Waddington Street, Norwich NR2 4JS, UK. Where appropriate half-tone photographs may be included and, where essential to illustrate important points, the Editor will consider the inclusion of colour figures (if pos- sible, authors should obtain funding to support the inclusion of such colour illustrations). As far as possible, review, return of manuscripts for revision and subsequent stages of the publication process will be undertaken electronically. For instructions on style, see the inside rear cover of Bulletin 124 (1) or the BOC website: www.boc-online.org ©British Ornithologists’ Club 2004 Apart from single copies made for the purposes of research or private study, or criticism or review, as per- mitted under UK law, no part of this publication may be reproduced, stored or transmitted in any form or by any means, except with prior permission of the publishers. Enquiries concerning reproduction outside these terms should be sent to the Editor; for address see inside rear cover. The Bulletin is despatched from the printer on publication and is sent by Surface Saver Postal Services to all European destinations outside the UK and by Air Saver Postal Services to destinations outside Europe. Those whose subscriptions have not been received by the beginning of a month of publication will have their copies despatched by surface mail, after their current subscription has been paid. Printed on acid-free paper. Published by the British Ornithologists’ Club Typeset by Alcedo Publishing of Pennsylvania, USA, and printed by Crowes of Norwich, UK il e,e@ pritish i he Ornithologists’ Club ave Volume 124 No. 4 December 2004 MEETINGS are normally held in the Sherfield Building of Imperial College, South Kensington, London SW7. The nearest Tube station is at South Kensington; a map of the area will be sent to members, on request. [Limited car parking facilities can be reserved (at a special reduced charge of £5.00), on prior application to the Hon. Secretary]. The cash bar is open from 6.15 pm, and a buffet supper, of two courses followed by coffee, is served at 7.00 pm. (A vegetarian menu can be arranged if ordered at the time of booking). Informal talks are given on completion, commencing at about 8.00 pm. Dinner charges are £19.00 per person but will be increased to £20.00 as from 1 January 2005. FORTHCOMING MEETINGS See also BOC website: http://www.boc-online.org 7 December 2004—Dr A.G. (Andy) Gosler—Eggshell maculation in the Great Tit and other passerines Andy Gosler has worked at the Edward Grey Institute, Oxford, since late 1981 when, having recently com- pleted an MSc in plant taxonomy, he assumed a part-time field assistant’s position ringing Great Tits in Wytham Woods. The BOU’s David Lack Studentship then funded his D.Phil. to study the evolution and ecol- ogy of Great Tit bills in Wytham Woods. Several important studies developed from that work. However, fas- cinated by the seemingly pointless patterns of pigment spots (maculation) on Great Tit eggs, in 1988 he start- ed recording and comparing the pigment patterns on eggs produced by different females. This ongoing study is yielding fascinating insights into how finely tuned are the breeding adaptations of these. Andy has been a member of both the BOU and BOC since 1976, and since 1998 has edited /bis. Applications to Hon. Secretary (address below) by 14 November please. 25 January 2005—Professor Glen Chilton—Lessons learned from the songs of North American sparrows and warblers Glen Chilton is an Associate Professor of Biology at St Mary’s College in Calgary, Canada. For the past 18 years most of his research efforts have concerned the songs of birds, particularly the evolution of songs in crowned sparrows and New World warblers. This work has taken him to some of the most remote areas of North America. Glen addressed the Club in September 2004 concerning the Labrador Duck and we are delighted to welcome him back to talk about his specialist subject. Applications to Hon. Secretary (address below) by 11 January please. 15 March 2005 (please note change of date)—Dr D. H. (David) Thomas—The shady life of birds David Thomas, Senior Lecturer in Zoology at the University of Wales, has specialised in the behavioural and physiological adaptations of birds in extreme environments, especially deserts—research on sandgrouse and phasianids in Moroccan Sahara, Negev, Namib and Sonoran Deserts as well as marine habitats—research on penguins in southern Africa and on shearwaters in the UK. Applications to Hon. Secretary (address below) by I March please. Future meetings in 2005—dates for further meetings in 2005 have been set for the following Tuesdays: 26 April (AGM), 7 June, 27 September, 1 November and 6 December. Speakers to be announced. Overseas Members visiting Britain are especially welcome at these meetings, and the Hon. Secretary would be very pleased to hear from anyone who can offer to talk to the Club, in 2005, giving as much advance notice as possible—please contact: Tony Statham, Woodcock Hill, Durrants Lane, Berkhamsted, Herts. HP4 3TR, UK (or e-mail: SAHS @tinyonline.co.uk). Registered Charity No. 279583 Club Announcements 221 Bull. B.O.C. 2004 124(4) Bulletin of the Vol. 124 No. 4 CLUB ANNOUNCEMENTS The Club regrets to announce the resignation (with immediate effect) of Mary Muller from her position as Vice-Chairman and as a member of the Committee. Cdr. Michael Casement will assume the respon- sibility of Vice-Chairman until the AGM in April 2005, as well as continuing his ex-officio role as Membership Secretary. , 2005 Subscription renewals—we are grateful to all members who have taken early action on the renewal notice enclosed with the September issue and have increased their Bankers Standing Orders (BSOs) for the new annual rates with effect from 1 January 2005. At the time of going to press (late October), approximately half have notified the Membership Secretary that amended BSOs have been dispatched to their banks and a fair number of remittances have now been received. If action is not already in hand, please do so now in order to minimise delays and unnecessary correspondence over the Christmas period. All queries to the Membership Secretary as soon as possible please (mbcasement @aol.com). The 925th meeting of the Club was held on Tuesday 28 September 2004, in the Sherfield Building Annexe, Imperial College, London. 23 Members and 8 guests were present. Members attending were: Dr C. F MANN (Chairman), Miss H. BAKER, Mrs D. M. BRADLEY, D. R. CALDER, Cdr. M. B. CASEMENT RN, Prof. R. A. CHEKE, Prof. G. CHILTON (Speaker), F. M. GAUNTLETT, D. GRIFFIN, C. A. R. HELM, J. P. HUME, D. J. MONTIER, MRS A. M. MOORE, Dr R. P. PRYS-JONES, R. J. PRYTHERCH, N. J. REDMAN, Dr P. G W. SALAMAN, S. A. H. STATHAM, C. W. R. STOREY, Dr D. H. THOMAS, M. P. WALTERS, R. P. WEBSTER and P. J. WILKINSON. Guests present were: M. J. BRADLEY, Mrs C. R. CASEMENT, Dr L. CHILTON, Mrs K. CHILTON, Mrs M. H. GAUNTLETT, Mrs M. MONTIER, P. J. MOORE and D. RUSSELL. After dinner, Prof. Glen Chilton outlined the unusual stories surrounding the now extinct Labrador Duck in an entertaining talk titled The curse of the Labrador Duck. The following is a brief synopsis. The North American Labrador Duck Camptorhynchus labradorius became extinct in the late-19th century. What we know concerning the natural history of the Labrador Duck is greatly exceeded by our ignorance, and the published literature contains many errors. It was a seaduck, and fed on small mussels, from sandy shoals. The species wintered along the American eastern seaboard, particularly in the waters around New York city. The only description of Labrador Duck nests comes from Audubon, who visited Labrador in July 1833; the account accompanies his painting of the species. However his diary explic- itly states that he found no Labrador Duck nests. Museums in Tring and Dresden have eggs thought to be those of Labrador Ducks, as does a private collection. DNA analysis has now been performed on all nine eggs to determine which, if any, were actually produced by Labrador Ducks. There are 53 stuffed specimens of Labrador Duck housed in 30 museums in 12 countries. One, in Germany, was destroyed by WWII bombing; many other specimens in England, France and Germany narrowly avoided destruc- tion at that time. One specimen is a reconstruction, using the bill of a Labrador Duck and the body of a white duck with black paint. Most specimens entered institutions before the era of detailed record keeping. Details of collection of some specimens are well documented, providing information about habitats used and the timing of migration. It is unclear why this duck became extinct. As a seaduck, it Club Announcements 222 Bull. B.O.C. 2004 124(4) may have been negatively influenced by raw sewage dumped into the ocean along the American eastern seaboard. Referees I am grateful for the invaluable contributions of the following persons, who have provided reviews of manuscripts submitted to the Bulletin during the course of my first year as editor (those who refereed more than one manuscript are denoted by an asterisk in parentheses after their name): Mark Adams, Axel Bratinlich, Michael Brooke, Dan Brooks, Bill Bourne, David Christie (*), Mario Cohn-Haft, Nigel Collar (*), Charles Collins, John Cooper, Mike Crosby, Andrés Cuervo, Jon Curson, Richard Dean, Ron Demey, Edward C. Dickinson (*), Bob Dowsett (*), Guy Dutson, Jonathan C. Eames, Brant Fairclough, James Ferguson-Lees, Jon Fjeldsa, Steven Gregory, Kees Hazevoet, David Holyoak, Niels Krabbe, Scott Lanyon, Curtis Marantz, Phil McGowan, Fabio Olmos (*), Fernando Pacheco (*), David Pearson, Alan Peterson, Theunis Piersma, Doug Pratt, Pamela Rasmussen, Van Remsen (*), Robin Restall, Craig Robson, Paul Salaman, Frank Steinheimer, F. Gary Stiles, Lars Svensson, David Wege, André Weller (*), and Andrew Whittaker.—THE EDITOR Marcos Pérsio Dantas Santos 223 Bull. B.O.C. 2004 124(4) New records of birds from the Brazilian state of Roraima by Marcos Persio Dantas Santos Received 26 Fuly 2003 Roraima is the northernmost state in Brazil, and has a total land area of 225,116 km’ and a population of c.325,000. Of these, 200,000 (61.5%) live in Boa Vista, the state capital (Barbosa et al. 1997), emphasising the state’s generally very low human population density. The naturalist Johan Natterer was the first person to con- duct ornithological investigations in Roraima (in 1831—1832). The majority of his collections were made along the rio Branco, especially around Sao Joaquim fort (Pelzeln 1871). Subsequently, in 1962 Olivério Pinto conducted an expedition to Roraima, traversing the rio Mucajai, and presented the first avian catalogue for Roraima, summarising bird collections made in the state (Pinto 1966). In recent decades, ornithological effort has been concentrated around Maraca Ecological Venezuela » Guyana Kennedy Ranch Ilha Inajatuba Ilha da Alianca Virua National Park headquaters iil Teal (i foul ae Highway “vicinal 29” se Roraima rivers Amazonas state (Brazil) 100 0 100 Miles a S| S Figure 1. Map showing localities in the state of Roraima mentioned in the text. Marcos Pérsio Dantas Santos 224 Bull. B.O.C. 2004 124(4) Station (Moskovits et al. 1985, Silva & Oren 1990) and the capital Boa Vista (Borges 1994). Stotz (1997) compiled the most recent checklist for Roraima, which included a total of 492 species, whilst more recently, Grosset & Minns (2002) pub- lished new data on Poecilurus kollari and Santos (2003) distributional information for Cercomacra carbonaria. I initiated research concerning birds in Roraima in January 2002. During this study I have made six visits to the state, each lasting 24 months and surveying seasonally flooded forest bordering the lower rio Branco, regions of higher land forest to the south and savannas to the north, close to the bor- der with Guyana (Fig. 1). My research has added five bird species new to the Stotz (1997) list and increased the total number of species recorded in the state to 497. All specimens have been deposited in the ornithological collection of the Museu Paraense Emilio Goeldi (MPEG), in Belém, Para, Brazil. Species accounts SAPPHIRE-RUMPED PARROTLET Touit purpurata On 10 August 2002, a male (MPEG 56276) was collected along the road leading to Virua National Park headquarters (01°29’N, 61°00’ W). The species is widespread through the Guianas, northern Brazil, south-west Colombia and eastern Ecuador (Forshaw & Cooper 1973), with the geographically closest records coming from Jai National Park (Borges et al. 2001) and areas north of Manaus (Cohn-Haft et al. 1997), both in Amazonas state. However, it had not previously been mentioned for Roraima. In Virua National Park, it proved to be relatively common, with groups of up to 25 individuals being observed. CHESTNUT-BELTED GNATEATER Conopophaga aurita On 2 February 2003, a male (MPEG 56879) was collected in the municipal district of Sao Joao da Baliza, on highway 29 (00°59’N, 59°52’W), in an area of high- ground forest (terra firme). Whilst this species is the most widespread of the genus (Sick 1997), it had not previously been recorded in Roraima. ZIMMER’S WOODCREEPER Xiphorhynchus kienerii Between 14 and 17 August 2002, five (MPEG 56325-56329) were collected on Ilha da Alianga (01°28’N, 61°15’ W), in the rio Branco adjacent to Virua National Park. This species has been found to occur exclusively in seasonally flooded forest (del Hoyo et al. 2003), and is common in such habitat on the Anavilhanas archipelago in the rio Negro (A. Whittaker pers. obs.) and at the mouth of the rio Jau (Borges et al. 2001). Given that this species exclusively occupies flooded forests and that there are no such forests north of Caracarai (01°50’N, 61°08’ W), this region may represent the northernmost limit for the species. For comments on this species’ tax- onomy see Aleixo & Whitney (2002). Marcos Pérsio Dantas Santos 225 Bull. B.O.C. 2004 124(4) ASH-BREASTED ANTBIRD Myrmoborus lugubris Between 13 and 14 August 2002, four (MPEG 56403-56406) were collected on Ilha da Alianga (01°28°N, 61°15’W), and three additional individuals (MPEG 56401, 56402, 56828) on Ilha de Inajatuba (01°25’N, 61°16’ W), in the lower rio Branco adjacent to Virud National Park. The species occupies flooded forests along the rio Napo in Ecuador, north-east Peru, south-east Colombia, in Brazil, along the rio Amazonas to the confluence with the lower rio Tocantins. Its presence in Roraima considerably expands the species’ known range from the closest-known localities of the archipelagos of Mariua and Anavilhanas, on the rio Negro (A. Whittaker pers. comm.). BLACKISH-GREY ANTSHRIKE Thamnophilus nigrocinereus Between 13 and 15 August 2002, five (MPEG 56351-56825) were collected on Ilha da Alianga (01°28°N, 61°15’W) and it is common on seasonally flooded islands in the lower rio Branco. The species is typically found in Brazil along the rios Negro and Amazon in areas of flooded forest (vdrzea), in forests along small streams and in igapo (black-water) flooded forests (Sick 1997). BLACK-CHESTED TYRANT Taenotriccus andrei On 24 January 2003 one (MPEG 56881) was collected at Fazenda Kenedy (02°40°N, 61°12’W), along the right bank of the rio Mucajaf. Only one bird was found, in a narrow band of degraded forest adjacent to pasture. Traylor (1979) already indicated the species’ presence in the state, based on specimens taken along the rio Padauiri, but as noted by Paynter & Traylor (1991) this locality belongs to the state of Amazonas, making my record the first for the species in Roraima. This species is very poorly known and is only sparsely distributed in the Brazilian Amazon (where it is principally known from the Tapajoés, Itaituba, Altamira and lower Xingu rivers, the forests around Belém and in northern Maranhao), as well as in southern Venezuela and probably Surinam (Ridgely & Tudor 1994). Acknowledgements I thank José Maria Cardoso da Silva for guidance, and Luis Fabio Silveira and Andrew Whittaker for critically reviewing the manuscript. My field studies were funded by Fundagao 0 Boticario de Protecao a Natureza (FBPN—050820012), WWF-Brazil—Ford Foundation (CSR 243-2001), Conselho Brasileiro de Desenvolvimento Cientifico e Tecnol6gico (CNPq) and the Instituto Brasileiro de Meio Ambiente (IBAMA). References: Aleixo. A. & Whitney, B. M. 2002. Dendroplex (=Xiphorhynchus) necopinus is a junior synonym of Dendrornis kienerii (= Xiphorhynchus picus kienerii) Des Murs 1855. Auk 119: 520-523. Barbosa, R. I., Ferreira, E. J. G & Castell6n E. G. (eds.) 1997. Homem, ambiente e ecologia no estado de Roraima. INPA, Manaus. Borges, S. H. 1994. Listagem e novos registros de aves para a regiao de Boa Vista, Roraima, Brasil. Bol. Mus. Para. Emilio Goeldi, sér. Zool. 10: 191-202. Marcos Pérsio Dantas Santos 226 Bull. B.O.C. 2004 1244) Borges. S. H.. Cohn-Hait. M.. Carvalhaes. A. M. P.. Henriques. L. M., Pacheco, J. F. & Whittaker. A. 2001. Birds of Jai National Park. Brazilian Amazon: species check-list, biogeography and conser- vation. Orn. Neotrop. 12: 109-140. Cohn-Haft, M.. Whittaker, A. & Stouffer, P. C. 1997. A new look at the “species-poor” central Amazon: the avifauna north of Manaus, Brazil. Pp. 205—235 in Remsen, J. V. (ed.) Studies in Neotropical ornithology honoring Ted Parker. Om. Monosr. No. 48. Forshaw, J. M. & Cooper. W. T. 1973. Parrots of the world. Lansdowne Press, Melbourne. Grosset, A. & Minns. J. 2002. Photospot: Hoary-throated Spinetail Poecilurus kollari. Cotinga 18: 114. del Hoyo, J., Elliott, A. & Sargatal. J. (eds.) 2003. Handbook of the birds of the world, vol. 8. Lynx Edicions, Barcelona. Moskovits, D. K.. Fitzpatick. J. W. & Willard. D. E. 1985. Lista prelimmar das aves da Estacao Ecolégica de Maraca, terit6rio de Roraima, Brasil, e areas adjacentes. Pap. Avulsos Zool. 36 (6): 51-68. von Pelzeln. A. 1871. Zur Ornithologie Brasiliens. A. Pichler, Vienna. Ridgely. R. S. & Tudor. G 1994. The birds of South America, vol. 2. Univ. Texas Press, Austin. Paynter, R. A. & Traylor. M. A. 1991. Ornithological gazetteer of Brazil. Mus. Comp. Zool., Cambridge, MA. Pinto. O. M. O. 1966. Estudo critico e catélogo remissivo das aves do Termiténo Federal de Roraima. Cadernos da Amaz6nia 8: 1-176. Santos, M. P. D. 2003. Novos registros do chorord-do-Rio-Branco (Cercomacra carbonaria) no estado de Roraima, Brasil. Atualidades Ornitolégicas 114: 3. Sick. H. 1997. Ornitologia brasileira. Ed. Nova Fronteira. Rio de Janeiro. Silva, J. M. C. & Oren, D. C. 1990. Resultados de uma excursao ormitolégica a ilha de Maraca, Roraima, Brasil. Goeldiana Zool. 5: 1-8. Stotz. D. F. 1997. Levantamento preliminar da avifauna em Roraima. Pp. 581—608 im Barbosa, R. L, Ferreira, E. J. G & Castell6n E. G (eds.) 1997. Homem, ambiente e ecologia no estado de Roraima. INPA. Manaus. Traylor. M. A. 1979. Checklist of the birds of the world. vol. 8. Mus. Comp. Zool., Cambridge, MA. Address: Universidade Federal do Piaui. Departamento de Biologia. TROPEN, Niicleo de Referéncia em Ciéncias Ambientais do Trépico Ecotonal do Nordeste, Av. Universitaria, 1310, Inmga, Teresina, Piaui. CEP 640449-550. Brazil. e-mail: persio@ufpi_br © British Omithologists° Club 2004 A record of Pale-legged Hornero Furnarius leucopus from Ecuador by Niels Krabbe Recetved 8 August 2003 On 2 February 2002, during field work on the eastern slope of the Cordillera de Cutucti in Morona-Santiago Province, south-east Ecuador, along a small tibutary of the rio Morona, near Unnsuantz (02°33°S, 77°54’ W. elevation 525 m), I collected a specimen of Pale-legged Hornero Furnarius leucopus. The specimen is now housed in the Museo Ecuatoriano de Ciencias Naturales, Quito (MECN 7647). There is no published specimen record of the species from Ecuador and north of the rio Marafidn in Peru, but J. V. Remsen, Louisiana State University, Museum of Niels Krabbe 227 Bull. B.O.C. 2004 124(4) Zoology (LSUMZ), kindly placed at my disposal the previously unpublished data of a series of six Peruvian specimens collected during expeditions by LSUMZ in dpto. Amazonas in 1978-1981, all of the widespread form tricolor. Two of these were collected along the rio Cenepa (near Huampami, 04°28°S, 78°10’ W, 200 m), and four along the rio Santiago (Caterpiza, 03°50’S, 77°40’ W, 200 m), suggesting that the species might also occur in the ornithologically unexplored Ecuadorian territory along these rivers. Field work in seemingly suitable habitat along the rio Pastaza (Kapawi, Isla Sharamentsa) in Ecuador, by myself and others, has failed to demonstrate the presence of this easily detectable species, suggesting that its Ecuadorian distribution is genuinely limited to the rivers further west. Although the Ecuadorian specimen has not been subspecifically allocated through direct comparison, it is undoubtedly referable to tricolor like the Peruvian specimens taken nearby. Address: Zoological Museum, University of Copenhagen, Universitetsparken 15, Copenhagen, 2100 Denmark, e-mail: NK Krabbe @zmuc.ku.dk © British Ornithologists’ Club 2004 A Syrian record: the case of Aharoni’s Thick-billed Larks Ramphocorts clotbey by Guy M. Kirwan Received 13 August 2003 Thick-billed Lark Ramphocoris clotbey is the sole representative of an attractive genus restricted to the Western Palearctic, where it breeds discontinuously, sparsely and, in some areas, erratically, from Morocco across North Africa to Jordan, north- central Saudi Arabia and, more irregularly, Kuwait (Snow & Perrins 1998). It was also mentioned for the ‘Syrian desert’ by Vaurie (1959) where, as detailed by Kumerloeve (1969a), two pairs were found in 1930 and, in 1931, a pair with four eggs. This information was repeated by Cramp (1988), but subsequently Baumgart (1995) considered that the records could not certainly be stated to have been made in modern-day Syria, and regarded the species’ occurrence in the latter country as unproven. Snow & Perrins (1998) added similar clarification; it might also be remarked that as early as 1970 Hiie & Etchécopar had questioned whether these records might definitely be considered as being from the Syrian Arab Republic. Given the species’ somewhat nomadic tendencies, it is perhaps surprising that Thick-billed Lark has apparently wandered so infrequently beyond its main range: there are several records from the Eastern Province of Saudi Arabia (Bundy ef al. 1989), a single mention for the former South Yemen (Hollom ef al. 1988), at an unknown location on 11 March 1962 (Warr unpubl. ms.), which was not included by Martins et al. (1996), an accepted record, in April 1999, in Oman (Eriksen & Guy M. Kirwan 228 Bull. B.O.C. 2004 124(4) Sargeant 2000) and a published claim of one in flight in the vicinity of the former Amik Goli, southern Turkey, in late May 1975 (Anon. 1976), a record which was not admitted to the list of birds reliably recorded in the country (Kirwan et al. 1999). Aharoni and the Syrian Thick-billed Larks What of the Syrian record? Kumerloeve (1969a) based his text on Aharoni (1931), who provided a detailed account of the discovery of the nest. However, neither proffered locality information. Prof. Aharoni was a Jewish zoologist of Lithuanian origin, who settled in Palestine and travelled extensively in the latter country and neighbouring regions until his death in 1946 (Warr 1996). His published contribu- tions included the most thorough account of the African Darter Anhinga rufa colony at Amik Golii (the former Sea of Antioch), now sadly lost, considerable information concerning Bald Ibis Geronticus eremita breeding places in Syria and many of our initial data for the breeding birds of the Syrian Desert (Aharoni 1928, 1929, 1930, 1931). Unfortunately, his reports were not always reliable or precise. As noted by Kumerloeve (1969b) and Baumgart (1995), there can be almost no doubt that Aharoni’s (1932) claim that the Cyprus Wheatear Oenanthe cypriaca had bred in Syria is false, whilst Safriel (1980) ably elucidated the problems associated with divining the whereabouts of Aharoni’s localities of Bald Ibis colonies in the same country, and Serra (2003) even suggested that over-reliance on these data had resulted in the latter species being erroneously considered to be extinct there. Baumgart (1995) did not present details as to why he considered the records as uncertainly appertaining to modern-day Syria, nor did he speculate as to which country the records might refer. With the post-World War One division of the Ottoman Empire and our knowledge of Aharoni’s wanderings, his records of Thick- billed Lark could pertain to Lebanon, Syria or Turkey. National boundary changes Under the terms of the May 1916 Sykes—Picot agreement, Britain and France established an advance agreement to divide the Levant between them upon the cessation of hostilities, with Britain assuming control of modern-day Iraq, Israel and Jordan, and Lebanon and Syria (collectively Greater Syria) being administered by the French. Problems soon arose, however, particularly in the French mandate, which also included the province of Alexandretta (the modern-day Hatay or Antakya province of southernmost Turkey). A special administrative system was designed for the latter under the Franco—Turkish agreement of Ankara, in 1921, and expanded boundaries for Lebanon were declared in September 1920. Indeed, even under the Ottomans, the region around Mount Lebanon had enjoyed a state of semi- autonomy since 1861. In 1926, as part of ongoing constitutional and governmental changes to Greater Syria, the French instituted Lebanon as an independent republic, although it remained under their control. During the period between 1920 and Guy M. Kirwan 229 Bull. B.O.C. 2004 124(4) official independence the country’s northern border was further north than its current position, encompassing the coastal strip as far as Latakia. In 1939, Alexandretta was finally ceded to Turkey, but despite strong Arab opposition to the French mandate, an independent Syria was not recognised until 1941 and this was not made official until 1946, whilst Lebanon only achieved such status three years earlier, in 1943 (Gilbert 1995, O’ Brien 2002, Goldschmidt 2002, Keay 2003). The specimens Aharoni (1931la,b) mentioned that his specimens had been sent to England, to Jourdain and Rothschild, and indeed, by chance, I located the two (one labelled a female and the other almost certainly a male, on the basis of size, much whiter- looking bill and more clearly demarcated cheek-spots, and the intensity and size of the black markings on the breast; see Keith et al. 1992, Svensson et al. 1999) in the Natural History Museum, Tring (accession numbers 1939.12.9.276 and 277; Fig. 1), and the label information confirms that they were taken at ‘El Zerka, in the north Syrian desert, on 6 April 1931’. Furthermore, the egg collection at the same institution contains two eggs collected by Aharoni at a locality named Dschukeil, Figure 1. Syrian specimens of Thick-billed Lark Ramphocoris clotbey held in the Natural History Museum, Tring (Guy M. Kirwan, copyright the Natural History Museum) Guy M. Kirwan 230 Bull. B.O.C. 2004 124(4) on 20 April 1931. Whether Aharoni found two nests is unclear, given the discrep- ancy in date and location and the information presented by Kumerloeve (1969a). The two-clutch hypothesis might appear more plausible, given the difference in dates and localities, and that Kumerloeve explicitly stated that ‘the’ nest had four eggs. However, a perusal of the specimen registers at Tring reveals that Aharoni was collecting at Baalbek and other sites in the Anti-Lebanon range on 20 April and the days immediately prior to and after this date, thus suggesting that an error was made in the registration or subsequently (see Knox & Walters 1992). Baumgart was apparently unaware of the existence of the specimens and eggs (M. Kasparek in litt. June 2003). Identifying the localities We now come to the issue of identifying the whereabouts of these localities. It is as well to bear in mind the various problems inherent to such research, which were discussed by Safriel (1980). However, from my readings of Aharoni’s published field work, it is equally important to note that he was not an uncritical or careless observer, despite some of the errors and problems outlined previously. In his writings, he consistently differentiated between Lebanon and Syria, rather than writing as if he were referring simply to Greater Syria. Thus, from the specimens register at Tring it is usually possible to identify in which of the modern-day countries Aharoni was collecting during a given period. Given Aharoni’s field work in the Hatay, it is possible that the records could have been made on Turkish soil. Neither El Zerka nor Dschukeil, even allowing for variant phonetics, is a Turkish name and both are absent from the most comprehen- sive gazetteer I have located (Burgett et al. 1984). Furthermore, I am unaware of any suitable habitat for the species in this region of Turkey (another factor mitigat- ing against the claim mentioned earlier in this note). At the time Aharoni made his observations, Lebanon comprised a slightly greater area than it does now. Irrespective of the obvious conclusion should Aharoni’s R. clotbey have emanated from the part ‘returned’ to Syria (Latakia), this possibility seems rather unlikely, given the habitat in the relevant region. As already mentioned, the possibility that Aharoni failed to distinguish between Lebanon and Syria appears somewhat remote. For localities of either name (or tangible variants), I searched the Syrian gazetteer available within an online database (http://www.nima.mil/gns/html/cntry_files.html). I located just two possibilities, both relating to El Zerka: Al Zirbeh (a town just south of Aleppo, now Halab, and relatively close to the Turkish border) and Al Zarga (just north of Al Raqga and much further east). Of these, the former would appear more probable, it being much closer to Aharoni’s known haunts and is in a region with suitable habitat for R. clotbey. However, my perusal of the Tring specimens register revealed that he also collected a juvenile Houbara Bustard Chlamydotis undulata (NHM 1939.12.9.242) and a Red-rumped Wheatear Oenanthe moesta (NHM 1939.12.9.219), among other species, at El] Zerka. The latter is unknown in Lebanon, and the former has been recorded just twice (Ramadan-Jaradi & Ramadan-Jaradi 1999). Even more importantly, the register also reveals that Aharoni was collecting in the well-known Qaryatein area one day prior to a March 1931 visit to El Zerka. This would definitely seem to place the Thick-billed Lark records within modern Syrian territory and prove that Roselaar (1995) was correct to consider the records to have probably come from the Qaryatein—Palmyra area, but also means that neither of the localities identified during the gazetteer search is likely to represent the collecting site of Aharoni’s specimens. Nonetheless, I enquired of Dr G. Ramadan-Jaradi (a Lebanese ornithologist) whether he knew of any localities similar to the names on Aharoni’s specimen labels. We eliminated two possibilities due to their location, but another merits full quotation of GR-J’s response of June 2003: “We also have...Ain El Zarka (34°21’N 36°22’E)...one of the springs which feeds Al Assi (Oronte) River. It is located on the western slopes of the Anti- Lebanon range, north of the Beqaa Valley, near Hermel. It is a semi-desert habitat where rainfall—partially inhibited by the high mountains—is just 250 mm pa. It is a direct extension of the Syrian Desert via the Homs depres- sion. Among the typical plants are Artemisia, Haloxylon, Salsola, Achillea, Scorzonera and Gymnarrhenea.” It is worth noting that the Thick-billed Lark is not mentioned for Lebanon (Ramadan-Jaradi & Ramadan-Jaradi 1999), but that semi-desert areas around Hermel have produced a number of ‘surprises’ in recent years including Mourning Wheatear Oenanthe lugens, Scrub Warbler Scotocerca inquieta (Bara 2002) and Temminck’s Horned Eremophila bilopha and Bar-tailed Desert Larks Ammomanes cinctura (Bradshaw & Kirwan 2000), some or all of which may be breeding there. On the basis of the above, R. clotbey is clearly worth searching for too. Whilst I consider that the available evidence suggests that Aharoni really did collect his specimens in modern-day Syria, the possibility that it might also occur in present- day Lebanon needs also to be considered. Acknowledgements The following offered invaluable assistance at the Natural History Museum (Tring): Mark Adams, Alison Harding, Robert Pris-Jones, Douglas Russell and Effie Warr. Mike Evans and Ghassan Ramadan-Jaradi made helpful comments concerning the whereabouts of Aharoni’s collecting localities. Max Kasparek and David Murdoch also assisted in the preparation of this short manuscript. I am grateful to Chris Feare for guiding this contribution through the editorial process. References: Aharoni, J.1928. Der Waldrapp, Comatibis eremita (L.). Orn. Beob. 26: 58-60. Aharoni, J. 1929. Zur Brutbiologische von Comatibis comata Bp. (Geronticus eremita L.). Beitr. Fortpfl. Biol. Vogel 5: 17-19. Aharoni, J. 1930. Brutbiologisches aus dem Antiochia-See. Beitr. Fortpfl. Biol. Vogel 6: 145-151. Guy M. Kirwan 232 Bull. B.O.C. 2004 124(4) Aharoni, J. 1931a. Brutbiologisches aus der Syrische Wiiste und dem Libanon. Beitr. Fortpfl. Biol. Vogel 7: 161-166, 222-226. Aharoni, J. 1931b. Drei neue Vogel fiir Palastina und Syrien. Orn. Monatsber. 39: 171-173. Aharoni, J. 1932. Bemerkungen und Ergénzungen zu R. Meinertzhagens Werk “Nicoll’s Birds of Egypt”. J. Orn. 80: 416-424. Anon. 1976. Recent reports. Orn. Soc. Turkey Bull. 13: 4. Bara, T. 2002. Bird notes from Lebanon, including two new species. Sandgrouse 24: 4445. Baumgart, W. 1995. Die Vogel Syriens: eine Ubersicht. Kasparek Verlag, Heidelberg. Bradshaw, C. G. & Kirwan, G. M. (compilers) 2000. Around the region. Sandgrouse 22: 156-160. Bundy, G., Connor, R. J. & Harrison, C. J. O. 1989. The birds of the Eastern Province of Saudi Arabia. H. EK. & G Witherby, London. Burgett, C., Rockmore, M. & Quinting, G. 1984. Gazetteer of Turkey, vols. 1-2. Defense Mapping Agency, Washington DC. Cramp, S. (ed.) 1988. The birds of the Western Palearctic, vol. 5. Oxford Univ. Press. Eriksen, J. & Sargeant, D. E. 2000. Oman bird list. The official list of the birds of the Sultanate of Oman. Oman Bird Records Committee, Muscat. Gilbert, M. 1995. The Routledge atlas of Jewish history. Routledge, London. Goldschmidt, A. 2002. A concise history of the Middle East. Westview Press, Boulder. Hollom, P. A. D., Porter, R. F., Christensen, S. & Willis, I. 1988. Birds of the Middle East and North Africa. T. & A. D. Poyser, Calton. Hiie, F. & Etchécopar, R. D. 1970. Les oiseaux du Proche et du Moyen Orient. Ed. Boubée, Paris. Keay, J. 2003. Saving the wind. The seeds of conflict in the Middle East. John Murray, London. Keith, S., Urban, E. K. & Fry, C. H. (eds.) 1992. The birds of Africa, vol. 4. Academic Press, London. Kirwan, G M., Martins, R. P., Eken, G & Davidson, P. 1999. A checklist of the birds of Turkey. Sandgrouse Suppl. 1: 1-32. Knox, A. G. & Walters, M. 1992. Under the skin: the bird collections of the Natural History Museum. Bull. Brit. Orn. Cl. Centenary Suppl. 112A: 169-190. Kumerloeve, H. 1969a. Recherches sur l’avifaune de la République Arabe Syrienne essai d’un apercu. Alauda 37: 43-58. Kumerloeve, H. 1969b. On the occurrence of the Pied Wheatear Oenanthe leucomela in Asia Minor and adjacent countries. Ibis 111: 238-239. 5 Martins, R. P., Bradshaw, C. G., Brown, A., Kirwan, G. M. & Porter, R. F. 1996. The status of passerines in southern Yemen and the records of the OSME survey in spring 1993. Sandgrouse 17: 54-72. O’Brien, C. K. (ed.) 2002. Philip’s atlas of world history. Philips, London. Ramadan-Jaradi, G. & Ramadan-Jaradi, M. 1999. An updated checklist of the birds of Lebanon. Sandgrouse 21: 132-170. Roselaar, C. S. 1995. Songbirds of Turkey: an atlas of biodiversity in Turkish passerine birds. Pica Press, Robertsbridge & GMB, Haarlem. Safriel, U. N. 1980. Notes on the extinct population of the Bald Ibis Geronticus eremita in the Syrian Desert. [bis 122: 82-88. Serra, G. 2003. The discovery of Northern Bald Ibises in Syria. World Birdwatch 25: 10-13. Svensson, L., Mullarney, K., Zetterstrom, D. & Grant, P. J. 1999. Collins bird guide. HarperCollins, London. Snow, D. W. & Perrins, C. M. (eds.) 1998. The birds of the Western Palearctic. Concise edition. Oxford Univ. Press. Vaurie, C. 1959. The birds of the Palearctic fauna. Passeriformes. H. F. & G Witherby, London. Warr, F. E. 1996. Manuscripts and drawings in the Ornithology and Rothschild Libraries of the Natural History Museum at Tring. British Ornithologists’ Club Occ. Publ. 2, Tring. Address: 74 Waddington Street, Norwich, Norfolk NR2 4JS, UK, e-mail: GMKirwan @aol.com © British Ornithologists’ Club 2004 Barry Taylor et al. 233 Bull. B.O.C. 2004 124(4) The nest, eggs and chicks of the White-winged Flufftail Sarothrura ayresi by Barry Taylor, Mengistu Wondafrash & Yirmed Demeke Received 4 September 2003 The genus Sarothrura (flufftails) is endemic to Africa and Madagascar and includes nine species of small rails (length 13.5—17 cm) which inhabit dense ground vegeta- tion of wetlands, grasslands, forest and dense bush (Taylor & van Perlo 1998). Most species are extremely shy and difficult to observe, and are usually located only by their very distinctive calls. Two species are classed as globally Endangered: Slender-billed Flufftail S. watersi of Madagascar and White-winged Flufftail S. ayresi of mainland Africa (Stattersfield & Capper 2000). The only known popula- tions of White-winged Flufftail occur in highland marshes near Addis Ababa, Ethiopia, and, 4,000 km to the south, in mainly highland marshes of eastern South Africa, where the species is regarded as Critically Endangered (Taylor 2000). Its total numbers are estimated at 210—215 pairs, confined to two marshes in Ethiopia, and 235 individuals in South Africa (Taylor & van Perlo 1998). In Ethiopia White-winged Flufftail breeds in July-August, in high-altitude seasonal marshes dominated by grasses, forbs and short sedges (Taylor & van Perlo 1998). The species is recorded from its breeding areas only in June—September, outside which period there is only one country record, from a lower altitude permanent marsh in May (Taylor 1994, Taylor & van Perlo 1998). South African records fall mainly in the period October-March inclusive, with isolated records in May, August and September, whilst there are also records from Zimbabwe in January—March 1977 and 1979, and one from Zambia in November 1962 (Taylor 1994, Taylor & van Perlo 1998). The species is assumed to migrate from Ethiopia to South Africa during the non-breeding season, as there is little overlap in occurrence dates between its two centres of distribution and also because there is no evidence that the species breeds anywhere in southern Africa, where it occurs mainly in tall, permanent reed and sedge marshes, which are very different to its breeding habitat in Ethiopia (Taylor & van Perlo 1998, BT unpubl. obs.). In Ethiopia, small numbers of this enigmatic species were recorded from 1939 to 1957 (Collar & Stuart 1985), after which no sighting was reported until 1984 (Massoli-Novelli 1988). In August 1995 the species was ‘rediscovered’ in small numbers at one of its traditional breeding sites (Atkinson et al. 1995). From 1996 to 1999, BT made annual visits to Ethiopia to study the species in collaboration with MW, YD and other field workers. This note describes the chicks, which were found in August 1996, and the nest and eggs, which were found in August 1999. Barry Taylor et al. 234 Bull. B.O.C. 2004 124(4) The nest and eggs The principal problem encountered in studying the breeding of this species is the vulnerability to disturbance and damage of the breeding sites, and the nesting habitat, by observers walking through the vegetation. The birds nest in rapidly growing vegetation only 20-40 cm tall (Taylor & van Perlo 1998), which is very susceptible to damage by trampling. The smaller of the two known breeding sites also suffers significant disturbance and damage by grazing livestock and by the cutting of growing Eleocharis sedges—the destruction of almost all of the bird’s once-extensive breeding habitat in the highlands near Addis Ababa has been largely due to overgrazing and sedge cutting (Taylor & van Perlo 1998, BT & MW unpubl. obs.). In view of the bird’s conservation status, and the importance of the only two known breeding sites for its survival, only very limited searches for nests were made, and great care was taken not to disturb any area more than once and to minimise the amount of damage caused by observers walking through the vegeta- tion. Finding and describing the nest and eggs was, however, deemed essential for two reasons: (1) to establish the precise nature of the nesting habitat, so that suitable areas could be located, protected and restored in currently degraded wetlands; and (2) to clarify the bird’s relationships with its congeners—for example, it had been suggested that this species lays patterned eggs (Taylor & van Perlo 1998), whereas all other flufftails lay pure white eggs. On 12 August 1999 a nest was found by YD and BT at a wetland site near Addis Ababa. The exact location of the site is not given in order to safeguard the wetland from disturbance. The nest was in a clump of mixed vegetation dominated by Eleocharis marginulata, a grass (probably Pennisetum schimperi) and a buttercup Ranunculus sp. It was placed about 1 cm above the substrate, on top of a small pad of Eleocharis stems, probably flattened by the bird, that were woven into the nest structure. The ground was largely flat and shallowly flooded to a depth of 1-5 cm and the nest was constructed in a clump of vegetation on a small, low ‘island’ of moist ground slightly above the water level. The vegetation in which the nest was built was 40-45 cm high and the surrounding vegetation was 30-45 cm high, in a continuous area of similar habitat near the edge of the wetland, about 60 m from the river running along the wetland margin. The nest (Fig. 1) was a ball of woven live Eleocharis and grass, with a few growing Ranunculus leaves woven into the outside. It was quite thickly lined with long pieces of dead grass and Eleocharis woven around the cavity walls. The circular entrance was at the side, near the top and at an angle of c.40° above the horizontal. It had Eleocharis stems protruding from its base and running down to the ground to form a rough ramp. The entrance faced towards the outside edge of the vegetation clump and the nest was very well concealed by surrounding vegetation, with live Eleocharis and Ranunculus forming a natural cover over and around it, except in front of the entrance, where there was a small open space just large enough for the bird to stand. There was no tunnel or track through the vegetation to the nest. Barry Taylor et al. 235 Bull. B.O.C. 2004 124(4) Figure 1. Left: the three eggs from the nest; right: White-winged Flufftail nest, Ethiopia, 12 August 1999 (B. Taylor) TABLE 1 Morphometrics of three eggs in the nest discovered near Addis Ababa, Ethiopia on 12 August 1999. Length Width Mass Calculated Calculated (mm) (mm) (g) volume (ml) density (g/ml) 27.2 19.8 5.47 5.44 1.007 27.3 20.0 5.65 5.57 1.014 27.8 19.9 5.78 5.6 1.030 The female came out of the nest as the observers approached, and walked 1.5 m away to stand on an open patch of flattened Eleocharis, from which it flew when the observers were less than 2 m away. A few minutes later a male was flushed c.20 m from the nest. Ethiopian Snipe Gallinago nigripennis were also nesting in this habitat, and we found over 20 nests of this species while searching for White- winged Flufftail nests. Nest dimensions (cm) were: outside height 17.5; outside width 15; entrance diameter 4.8; entrance height 5; thickness of walls and base 2.0—2.8; cavity diameter 9.8; cavity height 9.4. The nest contained three fresh eggs which were oval, white, smooth and slightly glossy (Fig. 1). One egg was collected and is deposited in the National Museum, Addis Ababa. Egg morphometrics are given in Table 1: volumes were computed from volume = 0.51*L*W2 where L = length and W = width (Hoyt 1979). Barry Taylor et al. 236 Bull. B.O.C. 2004 124(4) The nest was visited on 17 and 31 August when it held five incubated eggs, which were slightly visible through the nest walls (D. Kotze in litt.). When visited again on | September, by YD, the nest was empty with no sign of damage or distur- bance, indicating that the chicks had hatched successfully and that the incubation period was 15-16 days, assuming that one egg per day was laid from 13 or 14 August, and that incubation commenced when the clutch was complete. The chicks On 24 August 1996, BT visited the smaller breeding site with J. Atkins and S. Millington. While walking through very dense, continuous, 20—25-cm-tall vegetation flooded to a depth of 1-10 cm (most parts had at least 5 cm of standing water) and before dusk, at about 18.00 h, BT found a female White-winged Flufftail running through the vegetation, very unwilling to fly. All the observers stopped immediately and examined the ground, while the female ran around agitatedly. One small black downy chick was found sitting in a footprint on flattened grass. When picked up to ascertain whether it had been injured, the chick called repeatedly with loud, rather harsh cheeps. A second chick then began to call from another trampled spot, and was also picked up and examined. The female, attracted by the calls, ran around uttering quiet quacking notes and occasional quiet gulps and subdued, repeated grg and crk notes. A third chick was also found, but sadly it had been stepped on in dense vegetation as the observers approached; this chick was collected and is deposited in the ornithological collection of the National Museum, Addis Ababa. The two uninjured chicks were placed on the ground near the female, who led them into cover. Shortly afterwards a male flew from partially trampled vegetation c.30 m from the spot where the chicks had been found. A few minutes before this observa- tion, another chick, possibly from another brood, was heard calling in similar vegetation about 100 m away. The age of the chicks examined was judged to be two days, from observations of other flufftail species (Taylor 1994). The collected chick weighed 5.4 g and had black down, grey eyelids, blackish-brown eyes and grey-black legs and feet. The bill was shallowly conical with a chisel-like tip to the upper mandible; it had a pinkish-white base, a 1 mm-wide black vertical band immediately in front of the nostril, and an ivory tip. There was no egg tooth. The stomach contained Coleoptera (Dytiscidae) imagines, Diptera larvae (Tipulidae and Tabanidae), and the remains of small crustaceans. Discussion White-winged Flufftail is atypical of its genus in several respects: it has white secondaries (a character shared with the small rails of the genus Coturnicops of Asia and the Americas); it shows very reduced sexual dimorphism in the plumage; it apparently has a limited vocal repertoire and normally makes advertising calls Barry Taylor et al. Zoe Bull. B.O.C. 2004 124(4) only for a short period at dawn and dusk; it rarely responds to playback of its calls; and it is often easy to flush (Taylor 1994, Taylor & van Perlo 1998). Also, unlike other flufftails, when breeding it has never been heard to make any advertising or territorial call, or to respond to playback of any of its calls (Taylor & van Perlo 1998, BT unpubl. obs.). Its eggs and chicks are typical of the genus, and it is now clear that this species does not lay patterned eggs, as was suggested by Taylor & van Perlo (1998) on the basis of two unidentified clutches of patterned eggs found in cup-shaped grass nests in a seasonal wetland in Zimbabwe in the 1950s, and thought possibly to be flufftail nests (D. Parkes in Jitt.). White-winged Flufftail’s ball-shaped nest differs from those of other wetland and grassland flufftails such as Red-chested S. rufa, Streaky-breasted S. boehmi and Striped Flufftails S. affinis, which build a cup or bowl, sometimes with a loosely woven canopy of live vegeta- tion (Taylor & van Perlo 1998). Other flufftail species have a nest-building period of 2—3 days, usually lay eggs at daily intervals and incubate the clutch for 14—18 days (Taylor & van Perlo 1998). Assuming that White-winged Flufftail also takes 2—3 days to build its nest, the chicks seen on 24 August 1996 would have been hatched from eggs laid in the first few days of August in a nest constructed at the end of July. Only one week before this, on 24 July 1996, no White-winged Flufftails were seen at the site and the vegetation was deemed too short and sparse for occupation by the birds (J. Atkins in litt.), which presumably started nesting almost immediately after their arrival during the last week in July. The nest found on 12 August 1999 would probably have been built at the end of the first week in August; a visit by BT and YD to the site on 4 August showed that the vegetation was only just reaching the height and density to provide adequate cover for the birds, only two of which (both males) were flushed. The only other record of a young White-winged Flufftail is that of an unfledged juvenile collected at Sululta, Ethiopia on 22 September 1948 (Gadjacs & Keve 1968), and described in detail by Taylor & van Perlo (1998). This specimen is a male, well feathered on the head and body and with growing remiges. Based on the known growth rate of other Sarothrura species’ chicks (Taylor 1994), this bird is estimated to be about 16 days old, and was thus probably hatched from an egg laid in the third week of August. Our observations suggest that White-winged Flufftails begin to nest almost immediately after their arrival, which coincides with the development of the vegeta- tion to a height of 20-40 cm and before the ground becomes entirely flooded. This offers some support to the suggestion by Keith er al. (1970) that the migratory Streaky-breasted Flufftail may ‘represent the White-winged Flufftail ecologically’ in central and southern Africa. In this region, Streaky-breasted Flufftails begin nesting almost immediately after their arrival in temporarily inundated vegetation which, although grass-dominated, is often relatively sparse, of a similar height to that used by White-winged Flufftails in Ethiopia, and occurs on moist to shallowly flooded ground (Hopkinson & Masterson 1984, Taylor & van Perlo 1998). Barry Taylor et al. 238 Bull. B.O.C. 2004 124(4) Our observations also suggest that White-winged Flufftails move their chicks to more deeply and continuously flooded areas of denser vegetation very soon after hatching, and such behaviour might provide some degree of protection for the chicks, as the nest sites would be vacated before the vegetation had grown sufficiently to make it suitable for cutting by local people. The basic information on the breeding habitat, nest and eggs of White-winged Flufftail having been obtained, BT hopes that future work on this species in Ethiopia will give priority to locating new breeding sites and rehabilitating degraded wetlands to recreate suitable breeding habitat. Further disturbance of nesting birds to obtain more information on the nest and eggs would be unjustified, and the best method of obtaining detailed information on the breeding of this species would seem to be captive breeding, which has provided much important information for other wetland flufftails (Wintle 1988, Taylor 1994, Taylor & van Perlo 1998). Acknowledgements BT’s visits to Ethiopia were funded by the Middelpunt Wetland Trust (South Africa), the African Bird Club, the Zoological Society for the Conservation of Species and Populations, the South African Department of Foreign Affairs and the Sandton Bird Club (South Africa). We are very grateful to the Ethiopian Wildlife & Natural History Society (EWNHS), the Ethiopian Wildlife Conservation Organisation and Oxfam for the loan of vehicles and staff, and for much organisational and logistical assistance; we are especially grateful to Ato Tilaye Nigussie and Ato Abaye Assefa (EWNHS) and Ato Tesfaye Hundessa (EWCO) for their help and support. We thank Ato Akali Yemane, Ato Sileshe Dejene, Ato Tadesse Woldemariam Gole, Ato Tewabe Ashenafi, Dr Patrick Abbot, John Atkins, Donovan Kotze and Spike Millington for much help with field work. BT is especially grateful to John Atkins for his hospitality, advice and assistance in 1996. References: Atkinson, P., Robertson, P., Dellelegn, Y., Wondafrash. M. & Atkins, J. 1996. The recent rediscovery of White-winged Flufftails in Ethiopia. Bull. Afr. Bird Club 3: 34-36. Collar, N. J. & Stuart, S. N. 1985. Threatened birds of Africa and related islands. International Council for Bird Preservation, Cambridge. Gadjacs, M. & Keve, A. 1968. Beitrage zur Vogelfauna des mittleren Athiopie. Stuttgarter Beitr. fiir. Naturkunde 182: 1-13. Hopkinson, G. & Masterson, A. N. B. 1984. The occurrence and ecological preferences of certain Rallidae near Salisbury, Zimbabwe. Proc. V Pan-Afr. Orn. Congr.: 425-440. Hoyt, D. F. 1979. Practical methods of estimating volume and fresh weight of bird eggs. Auk 96: 73-77. Massoli-Novelli, R. 1988. Segnalazione di Schiribilla Alibianche, Sarothrura ayresi, in Etiopia. Riv. Ital. Orn. 58: 40-42. Stattersfield, A. J. & Capper, D. R. (eds.) 2000. Threatened birds of the world. BirdLife International, Cambridge, UK & Lynx Edicions, Barcelona. Taylor, P. B. 1994. The biology, ecology and conservation of four flufftail species, Sarothrura (Aves, Rallidae). Ph.D. thesis, Univ. of Natal, Pietermaritzburg, South Africa. Taylor, P. B. 2000. Whitewinged Flufftail. Jn Barnes, K. N. (ed.) The Eskom Red Data Book of birds of South Africa, Lesotho and Swaziland. BirdLife South Africa, Johannesburg. Taylor, P. B. & van Perlo, B. 1998. Rails: a guide to the rails, crakes, gallinules and coots of the world. Pica Press, Robertsbridge. Wintle, C. C. 1988. Crakes and flufftails in captivity. Unpublished MS. Bromley, Zimbabwe. Barry Taylor et al. 239 Bull. B.O.C. 2004 124(4) Addresses: Barry Taylor (corresponding author), School of Botany & Zoology, University of Natal, Private Bag X01, Scottsville 3209, South Africa, e-mail: taylorb@nu.ac.za. Mengistu Wondafrash, Ethiopian Wildlife & Natural History Society, P.O. Box 13303, Addis Ababa, Ethiopia. Yirmed Demeke, Institute of Biodiversity Conservation and Research, P.O. Box 32099, Addis Ababa, Ethiopia. © British Ornithologists’ Club 2004 Noteworthy ornithological records from Rondonia, Brazil, including a first country record, comments on austral migration, life history, taxonomy and distribution, with relevant data from neighbouring states, and a first record for Bolivia by Andrew Whittaker Received 4 September 2003 Located in the south-west of Brazil’s immense Amazon region is the state of Rond6onia. Rivers play a major role in the state’s geography with the rio Madeira dissecting the western section as it flows north-east into the Amazon. Furthermore, the borders with Bolivia are defined by the rios Mamoré, Guaporé and Branco. The state’s largest river, the Madeira, acts as a major barrier to many species of birds, animals and plants, which occur on only one side (Haffer 1992). Further east is the rio Tapaj6s, flowing north-east and forming another major physical barrier to species distribution. The area of land between these two major Amazon tributaries is known as the ‘Rond6nian area of endemism’, and contains many unique bird taxa (Haffer 1974, Cracraft 1985). The Rond6nian endemic centre encompasses almost all of Rond6nia, with the exception of the extreme west, on the left bank of the rio Madeira, bordering Amazonas and Acre. The presence of this rich endemic centre makes Rond6nia of very high conservation importance, due not only to the large number of endemics but also the extremely high indices of deforestation (Fearnside 1987, 1989). Thus the fauna and flora of Rond6nia are some of the most threatened within all of Brazilian Amazonia. Little has been published on the avifauna of Rond6nia. Natterer collected along the rios Madeira and Guaporé, whilst von Pelzeln (1868-1871) and Hoffmann concentrated along the lower rio Ji-Parana and rio Madeira (Hellmayr 1910). More recently, intensive ornithological field work was conducted along the middle rio Ji- Parana (or ‘Machado’ as it is known locally), at Cachoeira Nazaré (09°44’S, 61°53’ W) and Pedra Branca (10°02’S, 62°06’ W) by Stotz et al. (1997), resulting in Andrew Whittaker 240 Bull. B.O.C. 2004 124(4) ; Z 7 pA’ A Gs * h N A = ot ee bee reo 5 : M A O ~ Z a] a 4 ets KS >. ¢ J ‘= x "1! GROSSO } *~ y 11 s ee aes OF a : ‘| as RONDONIA >= ‘ rs. a l : a Set pee ee aati : 2, + ar aii DS Figure 1. Rond6nia illustrating the main survey sites and major collecting sites referred to in the text. State boundaries and major rivers are marked. Stars mark the study sites; 1) Paakas Palafitas Lodge, 2) Fazenda Rancho Grande, 3) Taquaras campina, 4) Cachoeira Nazaré, 5) Perda Branca, and 6) Parque Estadual de Guajara-Mirim. Note the scale is too small to depict either Palafitas Island or Nova Colonia. several noteworthy discoveries, including the remarkable Rond6énia Bushbird Clytoctantes atrogularis, new to science (Lanyon et al. 1990). Here I present important ornithological records made during field trips to Rondo6nia, including the first documented Subtropical Doradito Pseudocolopteryx flaviventris for Brazil and the first documented Pearly-breasted Conebill Conirostrum margaritae for Bolivia. Species accounts include life-history data for several little-known species (with additional non-Rond6nian data included where deemed important), comments on austral migrants, taxonomy and distributional information, including range extensions and new state records. References Andrew Whittaker 241 Bull. B.O.C. 2004 124(4) consulted for prior Rond6nian records, in addition to those already listed above, were (Peters 1940, 1948, 1951, 1968, 1979a,b, Pinto 1944, 1978, Ridgely & Tudor 1989, 1994, Whittaker 1996a). Austral migrants are species that breed in southern temperate South America and during the austral winter move north (Sick 1985, 1993, Chesser 1994). In general, such migrants arrive in Amazonia in March—May and depart in September—November. The presence of several austral migrants can be relatively hard to determine in Amazonia due to the existence of local resident populations; on arrival they merely augment existing populations and often go unrecorded. For example, Tropical Kingbird Tyrannus melancholicus is resident throughout Amazonia, making it near impossible to determine not only when austral migrant kingbirds arrive but also how many are involved, how long they remain and when they depart south. Often the only clue to the presence of migrants in Amazonia are flocks of 10—20 Tropical Kingbirds perched high in treetops along rivers during the austral winter (pers. obs.). Methods and study sites Survey work involved both audio and visual methods, with a significant emphasis on vocal identification. Voucher tape-recordings were made using a Sony TCM 5000 and a Sennheiser ME 66 microphone. All tape-recordings will be archived at the British Library National Sound Archive. Observations were made using 10 x 42 binoculars and by using playback to confirm visual identifications. Survey work focused on three main sites (Fig 1): five trips were made to Fazenda Rancho Grande, near Ariquemes, in 1989-1995; an eight-day rapid ornithological assessment of the Parque Estadual Guajara-Mirim was conducted in April 1995; and two visits to Pakaas Palafitas Lodge and the surrounding area were made, on 3-12 July 2002 and 18-26 June 2003. I also include opportunistic observations made en route from Porto Velho to Guajara-Mirim at Taquaras and along the rio Guaporé south of Pimenteiras do Oeste. Details of the survey sites and their vegetation are listed below. Fazenda Rancho Grande near Ariquemes (10°17’S, 62°52’W): primary upland terra firme forest, pastures and second-growth forest and some river-edge habitats. Continued deforestation in neighbouring fazendas has reduced the size of this forest and it has become more isolated from virgin forest. Parque Estadual de Guajard-Mirim (10°50’S, 64°85’ W): surveys were made along a recently cut road running east to the rio Formoso. Habitat consisted of primary upland terra firme with some river-edge, and microhabitats of Guadua bamboo and extensive dense vine tangles. Some small hills and bluffs occur in the terra firme, with rocky outcrops of 100-200 m supporting drier, stunted semi-deciduous forest. What appeared to be recent illegal entry had prompted road cutting, timber extrac- tion and hunting within the park’s boundaries. Andrew Whittaker 242 Bull. B.O.C. 2004 124(4) Paakas-Palafitas Lodge (10°51’S, 65°16’ W): situated 10 km south-east of Guajara- Mirim at the confluence of the rio Mamoré (white water) and the rio Pacaas Novos (black water). Based at the lodge, surveys were made in nearby upland terra firme, vdarzea and igapd, oxbow lakes, river bluffs, second-growth forest and cattle pasture. Much timber extraction and subsistence farming was evident (increasing in 2003) in nearby upland terra firme. However, large forest tracts are still connected to contiguous virgin forest. Palafitas Island (09°74’S, 65°13’ W): situated 5 km upriver of Paakas Palafitas Lodge on the rio Mamoré, an unnamed river island, which for my purposes here I refer to as Palafitas Island. Habitats included sandbars (at low water), mudbanks and succes- sional riparian habitats dominated by various pioneer plant communities and mature disturbed varzea. The island is uninhabited: although a small area of Cecropia and cane grass found burnt in 2002, the same area was undisturbed in 2003. Nova Colonia (09°01’S, 65°80’W): a small settlkement c.12—15 km along the rio Pacaas Novos with three families along a small left bank (black-water) tributary. Here I surveyed igapé and primary upland terra firme and second-growth forests. Taquaras campina (09°44’S, 65°13’W): near the small town of Taquaras. Here I surveyed campina forest (white-sand forest on a poorly drained sandy/clay soil) with stunted trees. Habitats Here I present a brief description of the various habitats and microhabitats that I surveyed and that are mentioned in the species accounts. Vegetation classification is based on Stotz et al. (1996), where more detailed floristic species lists typical of each habitat can be found. Forested habitats Tropical Lowland Evergreen Forests. Forests below 900 m, where rainfall is greater than 2,000 mm pa, grow where soils are suitable, sufficiently deep, well drained and never flooded. Upland terra firme forest has canopy heights of 30-40 m with emergents reaching 50-60 m and a closed canopy. The understorey was rather open and contained many spiny palms. Terra firme is renowned for the extraordinary diversity of plant species (Gentry 1990). Microhabitats found within these forests included Guadua bamboo, treefall gaps, vine tangles and stream sides. This forest type is the most abundant habitat and therefore the most commonly surveyed. Flooded Tropical Evergreen Forests. Flooded permanently or annually, most such forests are structurally and floristically similar to upland forests, but differ in supporting flood-tolerant trees and undergrowth plants. For more detailed informa- tion see Prance (1979). Andrew Whittaker 243 Bull. B.O.C. 2004 124(4) Floodplain vdrzea is found only along Amazonian white-water rivers and is flooded annually for several months. This habitat is sparse, being found only on Palafitas Island, where the canopy is 20-30 m with a typically open understorey and dense Heliconia patches, vine tangles and many bromeliads, with some human disturbance. Floodplain igapo forest is primarily found on sandy soils bordering black-water and clear-water rivers of Amazonia. Typically flooded for 5—6 months or longer p.a., this forest type occurs along the rio Pacaas Novos and its tributaries. At Novo Colonia it varied greatly, from tall forest with a 20-30 m-high canopy to a denser, lower 6-10 m-high canopy nearer the river. Both types have a very open understorey with few or no shrubs. Denser vine tangles were found along smaller streams and several areas of standing water. Filled-in floodplain lakes (swamp forests), in my survey refers to an oxbow lake containing several mature stands of Ficus and large clumps of Cecropia, and small- leafed bamboos at the edge of standing water. Around the lake are low stunted bushes, clumps of small trees, 5—10 m tall, and many flooded sedges. River-edge (and river island) forests. River-edge are early successional forests bordering rivers, and sometimes referred to as river bluffs. They replace riparian shrubby thickets and, in upper Amazonia, are regularly flooded, although run-off is rapid and vegetation is rarely submerged for more than a few days or weeks. This habitat contains stands of trees dominated by Cecropia, some Ficus and much Gynerium (Gramineae). River islands are dynamic, constantly changing size and shape. Thus, a variety of successional habitats can be found, depending on the age of the island (Remsen & Parker 1983). I surveyed a mature island, with vegetation types from cane grass, Tessaria, Mimosa and Salix scrub, clumps of Cecropia and 20-30 m-tall mature vdrzea with some vine tangles. Gallery forests. These occur along watercourses throughout drier regions (annual rainfall less than 1,600 mm), where other conditions (e.g. fire) inhibit the growth of woody vegetation away from the rivers. White-sand forests. Forest and scrub on white sand in Amazonia. These occur very patchily, covering c.60,000 km in Brazil (Pires 1974). Overall structure and composition varies greatly between sites, depending on soil type and drainage. Typically, most white-sand soils in Brazil contain virtually no clay; nutrient levels are extremely low and water retention poor. However, in my study area white-sand forests occur on weathered clays with poor drainage (pers. obs.). Edaphic conditions, especially drainage, considerably affect vegetation structure and composition (Gentry 1988). Plant endemism is high in these campinas, but plant diversity is low (Anderson 1981). Such white-sand forests are referred to as varillal or very low-stature chamizal in Peru (Alvarez Alonso & Whitney 2003). Andrew Whittaker 244 Bull. B.O.C. 2004 124(4) Campina is rather open scrub, with only small shrubs and trees (4-12 m), and patches of bare sand, which are usually well drained. I surveyed poorly drained campina on white-sand weathered clay at Taquaras campina, which has a 10-12 m canopy and adjacent taller campinarana. Low tree species diversity occurs in both areas. The campina has melastomes dominating the fairly open understorey, where small patches of low terrestrial bromeliads most frequently occur in the lower wetter areas. Campinarana is closed-canopy woodland taller than campina, which often occurs adjacent to campina where soils with more nutrients and better drainage exist. This, in turn, is surrounded by upland terra firme, where soils are richer still, with the transition being gradual (pers. obs.). The Taquaras site has a closed canopy of 12—18 m with an open understorey and few or no shrubs. Palm forests. Small to extensive stands of Mauritia flexuosa in poorly drained areas within savannas, at lake edges or along streams in Amazonia. Second-growth forests and woodlands. Two types were surveyed: tall second growth dominated by Cecropia and lower shrubby vegetation dominated by Vismia spp. The latter is sometimes described as second-growth scrub. Non-forest habitats Cerrado is distinctive savanna vegetation, with tall grass and scattered low, gnarled trees. In areas of denser tree cover it is known as cerraddo. This habitat occurs mostly in central Brazil, adjacent eastern Bolivia and north-east Paraguay. Species accounts AGAMI HERON Agamia agami S. L. Hilty and I observed an adult and an immature at an overgrown oxbow lake at Paakas Palafitas Lodge. In response to my close approach a low guttural series of notes, presumed to be an alarm call, was repeated and st -recorded. Zimmer & Hilty (1997) reported what must be the same voice as uur’ r’r’r’ from Amazonas, Venezuela. This unobtrusive species was recorded by Stotz et al. (1997) as rare along the middle rio Jiparana. LEAST BITTERN Jxobrychus involucris A single vocalising bird was tape-recorded at an overgrown oxbow lake at Paakas Palafitas Lodge by S. L. Hilty and myself on three evenings between 20 and 25 June 2003. This apparently represents a new state record. The Amazonian distribution of the species is poorly understood as it inhabits dense marshes and, unless vocal, is easily overlooked. Andrew Whittaker 245 Bull. B.O.C. 2004 124(4) ORINOCO GOOSE Neochen jubata At least two territorial pairs were present at Palafitas Island, in the rio Mamoré, during July 2002 and June 2003. Birds were tape-recorded and observed entering forest, where they were presumed to be nesting in July 2002. Reported as rare on the middle rio Jiparana (Stotz et al. 1997). Once widespread in Brazil, Orinoco Goose is now extremely rare and very local, and mostly encountered along remote waterways with low human populations and little or no hunting pressure. In areas such as along the middle rio Jurua flocks of up to 20 were not uncommon in 199] (Whittaker & Oren 1999). ZONE-TAILED HAWK Buteo albonotatus An adult observed mid-morning on 11 July 2002 outside Guajara-Mirim, soaring over a small serra 2 km east of the town. This is apparently the first record for Rondonia. There are few records from Amazonian Brazil, the closest being from Acre, at Cruzeiro do Sul, and along the upper rio Jurua at Porto Walter (Whittaker & Oren 1999). ROADSIDE HAWK Buteo magnirostris Surprisingly, in 2003 two subspecies were observed sympatrically at Paakas Palafitas Lodge, the darker B. m. saturatus and paler B. m. magnirostris. In plumage the darker saturatus was easily identified by its characteristic blackish hood, dark brown upperparts, white eye and cinnamon-rufous barring below, whereas magnirostris 1s distinctly paler above with a grey back and head, yellow eye, grey upper breast and finer tawny barring below. These differences were obvious in the field, where saturatus was the commonest form, with 2—4 seen daily. I recorded only one adult magnirostris, on 22 June 2003, perched beside the rio Pacaas Novos. In Brazil saturatus occurs in Acre, Mato Grosso do Sul and Mato Grosso (Pinto 1978), with magnirostris throughout Amazonian Brazil. However, on 23 and 25 June 2003, I observed two adults intermediate between these two subspecies unidentified to any race or age-related plumage. This observation suggests interbreeding where the two forms are sympatric. Possibly saturatus has recently colonised Rondonia from the south, following rapid deforestation in recent decades, permitting the two forms to come into contact. Further research around Guajara- Mirim is essential to clarify if the two subspecies do interbreed. LONG-WINGED HARRIER Circus buffoni A dark-morph adult was videotaped quartering over early-successional growth at Palafitas Island on 10 July 2002. This appears not only to be a new state record but also the first for Amazonian Brazil, and certainly represented an austral migrant. Austral migrants in Brazil are principally known from Rio Grande do Sul and Santa Catarina (Sick 1985), but the nearest records to Rond6nia are from Mato Grosso, in the northern Pantanal, and Chapada dos Guimaraes where this harrier is present only during the austral winter (pers. obs.). Andrew Whittaker 246 Bull. B.O.C. 2004 124(4) CRYPTIC FOREST-FALCON Micrastur mintoni This recently described species (Whittaker 2002) was observed and tape-recorded in terra firme near Paakas Palafitas in June 2003 and at Nova Colonia in July 2002. It was also recorded in seasonally flooded igapé and in second growth bordering terra firme at Novo Colonia. Two specimens, previously identified as Lined Forest- falcon M. gilvicollis, from Cachoeira Nazaré (Stotz et al. 1997) are, in fact, mintoni (pers. obs.). Lined Forest-falcon occurs in Rond6nia only west of the rio Madeira, in terra firme (Whittaker 2002). ORANGE-BREASTED FALCON Falco deiroleucus I located an adult (presumed male) of this rare falcon on 15 July 2000, while leading a bird tour with S. L. Hilty, on the rio Guaporé, south of Pimenteiras do Oeste, Rond6nia. This is seemingly the first state record, with the nearest known records being from Mato Grosso, where K. J. Zimmer and I observed an adult at Chapada dos Guimaraes on 13 September 1996. For many years, Orange-breasted Falcon was considered absent from central Amazonia (Cade 1982), but recent reports have confirmed that it inhabits central Amazonian Brazil (Whittaker 1996b). The Rond6nian record and other unpublished Amazonian records confirm this: K. J. Zimmer and I observed what was presum- ably the first record for Roraima, a subadult on a river island in the rio Branco, 6 km north of Boa Vista, on 1 November 1994, and also an adult male at the Serra dos Carajas, Para, in February 2003. Documented hunting attempts and prey of F. deiroleucus are few. S. L. Hilty and I observed the male still-hunting from the crown of a dead 25—30 m emergent on a river bluff of the rio Guaporé. The falcon launched itself from the 25 m-perch in very fast direct flight, initially in a sharp 45°-dive until it reached c.10 m above the water, where it adopted powerful horizontal dashing flight for c.350-400 m towards a Great Kiskadee Pitangus sulphuratus. The flycatcher was flying across the river, but presumably noted the approaching falcon and thus evaded its upward stoop. The falcon thereafter immediately returned to its original perch. This had been assumed to be the most common hunting technique (Bierregaard 1994). Prey are mostly medium-sized to large birds, including pigeons, parrots, parakeets, swifts and martins (Bierregaard 1994), but smaller prey such as insects have been recorded (Whittaker 1996b). I also confirmed an adult female taking a Crested Oropendola Psarocolius decumanus from a photograph taken by Jackie Dann, in Bolivar, Venezuela. LARGE-BILLED TERN Phaetusa simplex I observed this common and widespread species on several occasions following both Tucuxi Sotalia fluviatilis and Amazon River Dolphin /nia geoffrensis pods along the rio Mamoré at Paakas Palafitas Lodge. Birds were seen plunge-diving near these dolphins and taking fish disturbed by the dolphins or pieces of fish left by them. I have noted this behaviour frequently throughout Amazonian Brazil on Andrew Whittaker 247 Bull. B.O.C. 2004 124(4) all major rivers, where the birds follow dolphins for long periods swooping or plunge-diving for prey disturbed by them. Large-billed Terns seem to more frequently engage in this behaviour when following the larger /nia geoffrensis, although further observations are needed to quantify this. CRIMSON-BELLIED PARAKEET Pyrrhura perlata Regularly observed in small flocks at Fazenda Rancho Grande by K. J. Zimmer and myself. In late-January 1995 six including two apparent immatures were observed food begging (head-bobbing). The immatures mostly differed in lacking the bold crimson belly, instead showing just a few sparse crimson feathers on the belly. Crimson-bellied Parakeet is sympatric with Hellmayr’s Parakeet P. amazonum (Joseph 2002), a Brazilian endemic, at all three sites but was the less common of the two. Flight calls of these Pyrrhura are so similar, and vary according to the number of birds calling, that the less common Crimson-bellied can be overlooked. However, when Crimson-bellied Parakeet vocalises from a perch it is fairly easily separated by voice from Hellmayr’s Parakeet, instead sounding most similar to Pearly Parakeet P. lepida. RUFOUS-VENTED GROUND-CUCKOO Neomorphus geoffroyi This rarely seen species was observed on three occasions for a total of c.20 minutes in terra firme at Parque Estadual de Guajara-Mirim, on 24—25 April 1995. During my observations I noted the following details: mantle glossy green, wings greenish with purplish flight-feathers, tail (in good light) metallic purplish with metallic greenish tips, forehead scaled buff-brown, hindcrown metallic green and hindneck boldly scaled green with less obvious pale buff, heavy buff scaling reaching to the black breast-band, and below plain buff with a rufous ventral area. Soft parts: irides dull creamy white, bill horn and legs grey. Only after three close views was I able to note the bird’s bright blue bare post-orbital skin; thus, this field mark could be easily overlooked in shaded forest understorey. My plumage description most closely accords with nominate geoffroyi, which is known from specimens taken along the rio Madeira at Calama and Maruins (Peters 1940). Little has been published on the behaviour of this species. I initially observed it foraging on the forest floor below an understorey mixed-species flock of antshrikes (Thamnomanes, Thamnophilus), antwrens (Myrmotherula) and Rose-breasted Chat Granatellus pelzelni. The Neomorphus was confiding when I was still, but any movement would cause it to raise and depress its long, glossy metallic green crown feathers. I also observed the bird scratching its large bill with its feet, rather like a domestic chicken. It kept entirely on the forest floor, where it walked slowly and deliberately, and without warning would suddenly run at great speed (quicker than anticipated), before abruptly pausing to catch unidentified prey in the leaf litter. The running bird was extremely fast and agile, even moving thus through dense vine tangles. It also habitually lowered the head from the normal position just before running until it stopped. The ground-cuckoo seemed to prefer the thick cover of Andrew Whittaker 248 Bull. B.O.C. 2004 124(4) fallen vine tangles, which are fairly widespread in parts of this forest. Once I saw the bird crouch on the ground, quivering its wings and opening the bill, perhaps suggesting the presence of a second bird. The voice of the nominate form, to my knowledge, is unknown. I only twice heard loud bill-clapping when the bird ran directly towards me, to within 3 m. I played the voice of Rufous-winged Ground-cuckoo N. rufipennis without eliciting any response. Further research is urgently required to properly assess species limits and basic ecological requirements among this ground-cuckoo’s disjunct taxa. Significant habitat destruction is occurring or has occurred throughout the species’ range, particularly where N. g squamiger (in the lower rio Tapajés), N. g. maximiliani (Bahia) and N. g. dulcis (Espirito Santo to Rio de Janeiro) occur. All are Brazilian endemics and warrant immediate research and conservation attention. Documentation of the threatened Banded Ground-cuckoo N. radiolosus from Ecuador and Colombia in lowland terra firme confirms this species to be extremely sensitive to habitat disturbance (Collar et al. 1992). BURROWING OWL Speotyto cunicularia One was observed along the road from Porto Velho to Fazenda Rancho Grande, on 24 January 1995, and at least two pairs in cattle pasture near Paakas Palafitas Lodge, daily in June 2003. The species is presumably a recent colonist in Rond6nia following large-scale deforestation that has transformed vast areas into cattle pasture. I am unaware of any previous records from the state, and my observations appear to the first. Very few records are available for this open-country owl from rainforest areas in the Amazon basin. The closest are both from Amazonas, where deforestation has made way for large-scale cattle ranches, mostly south of the Amazon. However, north of the Amazon, some 80 km north of Manaus, a resident individual was located at one of three large 15,000-ha partially deforested cattle ranches, during 1992 to 1994 (Cohn-Haft et al. 1997), and south of the Amazon I recorded a pair 35 km south of Careiro, on 28 September 2003. SAND-COLOURED NIGHTHAWK Chordeiles rupestris A flock of 50+ was present on recently exposed sand and mudbanks on Palafitas Island, in the rio Mamoré, in both July 2002 and June 2003. Water levels were falling (an annual event at this season), and these usually silent, crepuscular birds were very vocal and active even in mid afternoon, as nest sites on exposed sandbars became available. Displaying males were chasing one another and calling loudly in flight. Displaying birds were easily recognised as males, as on landing they revealed their striking white throats while uttering their rather musical gurgling songs. NACUNDA NIGHTHAWK Podager nacunda A lone bird was observed day-roosting on a sandbar on Palafitas Island on 10 July 2002. Upon my approach the bird opened its eyes, raised its head and fluffed out its Andrew Whittaker 249 Bull. B.O.C. 2004 124(4) throat, revealing its white throat patch (confirming it to be a male). It then proceeded to give a single deep gruff call, which was repeated every 7—10 seconds before it flushed, landing c.30 m distant. The species is a well-known austral migrant to Amazonia (Sick 1985) and I assume this individual too was an austral migrant. Nearest breeding records are from northern Mato Grosso, where I have recorded breeding in September at Chapada dos Guimaraes (unpubl. pers. obs.). SILKY-TAILED NIGHTJAR Caprimulgus sericocaudatus This little-known nightjar was tape-recorded at Parque Estadual Guajara-Mirim on the clear moonlight night of 25th and dawn of 26 April 1995. Four to five well- spaced birds were heard singing in primary upland ferra firme dotted with a few bare rocky outcrops. This record appears to represent the first for Rond6nia. In response to playback, a bird flew 150-200 m from a forest clearing and landed c.8—12 m above me in a tall sapling. This male then started singing from a fairly concealed perch, a rather melodious two-note call, repeated monotonously every 1-2 seconds for periods of up to three minutes. The bird tossed its head slightly upwards when singing. It was noted to be overall dark, but I noted a distinct broad rufous collar and heavy white spotting on the upper breast. Comparisons with tape-recordings of nominate sericocaudatus from Argentina and mengeli from Ucayali, Peru (Hardy et al. 1989), confirmed the Rond6nian birds to pertain to the latter. Subspecies mengeli is known from very few Brazilian locali- ties, with Amazonian specimens from Santarém, Para (Pinto 1978, Sick 1985), and I tape-recorded a singing male at rio Cristalino, Alta Floresta, Mato Grosso, at a clearing in primary upland terra firme. This is the sole record during 15 years of intensive field work at the site (pers. obs). SCISSOR-TAILED NIGHTJAR HAydropsalis brasiliana An adult male was almost overlooked as a Ladder-tailed Nightjar H. climacocerca when flushed from a day roost on Palafitas Island on 10 July 2002. The bird was disturbed from low bushes in early-successional growth and flushed c.10 m to perch on an exposed horizontal branch | m above ground in a young sapling. The species probably undertakes rather local movements or perhaps some are austral migrants, as it is not usually found on Amazonian river islands. Along the rio Mamoré, as in most of Amazonia, H. climacocerca is the common riverine nightjar, being often fairly numerous on white-water river islands (pers. obs.). Movements of H. brasil- iana are poorly known in Brazil, but the race furcifera disappears from many areas of Rio Grande do Sul during the austral winter (Belton 1984). LONG-TAILED POTOO Nyctibius aethereus One heard on 28 January 1995 in terra firme at Rancho Grande, Ariquemes. Reported to be a rare resident by Stotz et al. (1997) at Cachoeira Nazaré from river- bluff forest. Unless its vocalisations are known and nocturnal surveys undertaken this low-density species easily goes unrecorded. Andrew Whittaker 250 Bull. B.O.C. 2004 124(4) LESSER SWALLOW-TAILED SWIFT Panyptila cayennensis A pair was observed roosting in a nest positioned under a building beside the rio Mamoré, at Paakas Palafitas Lodge, in late-June 2003. The nest was a c.1-m-long vertical, straight tube with a diameter of 10-12 cm and the entrance at the bottom, located 12 m up on the underside of a large cement roof supported by stilts. The nest was constructed of yellow plant fibres neatly cemented together. Nesting in Brazil was recorded by Sick (1985), who reported nests attached to tree trunks and even on a roof inside a house. I observed a nest in Alagoas in January 2004, located in the apex of the eves of a chalet. Sick (1947) also stated that nest length varies from 30 cm to | m. RUFOUS-NECKED PUFFBIRD Malacoptila rufa Only two records of this rarely encountered and poorly known puffbird were made, in terra firme understorey at Rancho Grande, in May 1990, by R. S. Ridgely, G Tudor and myself, and by K. J. Zimmer, on 29 January 1993. Stotz et al. (1997) recorded this puffbird as common at both Cachoeira Nazaré and Pedra Branca. However, this included mist-net captures (1,450 mist-netting days). Mist-netting is one of the most reliable methods of censusing these forest puffbirds, enabling a true impression of their abundance (pers. obs.). Little is known about the behaviour of Rufous-necked Puffbird. Singles or widely spaced pairs still-hunt from perches, normally at 2-10 m, occasionally higher, within forest, and if flushed fly silently in a normally straight line before landing 15-20 m distant. On landing they slightly spread their tail-feathers and nervously jerk the tail sideways (either to left or right) from the normal vertical position. These movements continue until the tail is c.15—20° from the vertical, and then return to the latter, before jerking 15—20° to the opposite side. Similar behaviour has been noted among nunlets Nonnula (Whittaker et al. 1995), and continues while observers are nearby. Such behaviour might be used to visually communicate danger between pairs (pers. obs.). Their still-hunting behaviour, combined with the fact that this puffbird seemingly vocalises infrequently (or only for short periods, especially around dawn and dusk) and its voice is quiet (and easily overlooked as an insect), means that the species is very easily missed during field surveys. The voice is also poorly known. I tape-recorded what I presume to be the song of the subspecies brunnescens, first at Alta Floresta, Mato Grosso, on 12 November 1996, and subsequently twice along the rio Roosevelt, Amazonas, a series of high, thin notes forming a 4—5-second metallic trill (slowing slightly at the end), repeated every 20—25 seconds, which is similar to the only description of the species’ voice (Zimmer et al. 1997). This loudsong is similar to that of White-whiskered Puffbird M. panamensis and could be overlooked as an odd-sounding Golden-crowned Spadebill Platyrinchus coronatus song at distance (pers. obs.). Both K. J. Zimmer (pers. comm.) and I, using a copy of my recording, have solicited silent perched M. rufa in Mato Grosso (nominate) and in Amazonas to respond using the same vocali- Andrew Whittaker 251 Bull. B.O.C. 2004 124(4) sation. I also recorded a different voice in response to playback of the song, from two territorial birds along the rio Roosevelt. This voice was a louder series of fast trilled notes, with an emphatic and abrupt, louder final note, quickly repeated 8—9 times during an |1-second period, and given once or occasionally twice immedi- ately following playback of the loudsong. The two birds approached me to within a few metres in the understorey. I assume agitated birds at territorial boundaries use this voice naturally. During their approach I noted that they seemed to puff out the breast feathers, making their striking pure white upper-breast patches appear larger and more prominent in the poorly lit understorey. Such behavior might be used in territorial disputes. Several other forest-dwelling Malacoptila have white upper- breast patches and inhabit the dark understorey of tropical forests (pers. obs.). Call notes of M. rufa are described as a high, thin descending seeee... (Zimmer et al. 1997), almost identical to alarm calls I have noted from Semi-collared M. semicincta, Crescent-chested M. striata, White-chested M. fusca, White-whiskered and Black-streaked Puffbirds M. fulvogularis (pers. obs.). K. J. Zimmer (pers. comm.) observed a bird at Rancho Grande attending a small swarm of Labidus ants also attended by Black-faced Antbird Myrmoborus myotherinus, Scale-backed Antbird Hylophylax poecilinota and a pair of Warbling Antbirds Hypocnemis cantator, but no obligate ant followers. I also observed this puffbird feeding at the head of a large Eciton ant swarm at Amazonia National Park, Amazonas, with many obligate antbirds in attendance, including Harlequin Antbird Rhegmatorhina berlepschi and Black-spotted Bare-eye Phlegopsis nigromaculata, as well as Barred Forest-falcon Micrastur ruficollis and Dark-winged Trumpeter Psophia viridis. There are apparently no recorded breeding observations of this puffbird. In upland terra firme at the rio Cristalino, Mato Grosso, on 8 September 2000 and 4 August 2003, after flushing birds from the forest floor, I located two nest burrows. The first was in a large bamboo patch only a few metres from a well-trodden trail. The second was in patchy bamboo and vine tangles just 30 cm from an infrequently used trail. Both were in flat terrain but the burrow entrance was constructed on a slight gradient. As in other Malacoptila the entrance was reinforced by c.30—50 dry, dead twigs of 2—10 cm, although one was 30 cm long. I have also noted such nest protection in White-chested and Crescent-chested Puffbirds, and Stiles & Skutch (1989) recorded it in Costa Rica for White-whiskered Puffbird. As well as offering at least some protection from erosion, I suggest that these sticks around the entrance may act as deterrent against terrestrial predators such as snakes. In passing over the twigs they would possibly be more likely to overlook the nest than if it was a bare- sided hole on the open forest floor. Thus, these twigs possibly help reduce nest predation, increasing nest success. I was unable to confirm if the first nest had eggs or young, but the August nest contained two c.7—9-day-old chicks, just in pin with their eyes open. I measured the nest tunnel, which was oval-shaped at the exit and c.8 x 5 cm. The burrow sloped Andrew Whittaker 252 Bull. B.O.C. 2004 124(4) gently down and back for c.75 cm, where it curved right, and the nesting chamber was visible, with a small amount of dry vegetation in the cup lining. CHESTNUT JACAMAR Galbalcyrhynchus purusianus Known in Brazil only from the upper rio Purtis and rio Jurua, Acre (Sick 1993). My records represent both a significant range extension and the first east of the rio Madeira. The oxbow lake behind Paakas Palafitas Lodge held a resident territorial family group of six observed daily in both years. Birds were always perched on prominent vantage points, sometimes with all group members in the same tree. Still-hunting was mostly from exposed horizontal branches, often from some of the most- exposed tall trees at the edge of the vdrzea or in lone trees within the flooded oxbow. Preferred perches seemed to be in open trees, such as Cecropia, affording opportunities for the mostly horizontal sallies after insects. Most sallies were over 4—8 m, but some of 20-30 m were observed. Following sallies, individuals mostly returned to the initial perch. All identified prey were Hymenoptera wasps, bees and sweat bees. Playback of their voice resulted mostly in the entire group, one by one, flying in to investigate (often from some distance). Upon landing, often on the same branch, they perched side by side and gave long excited rattle calls, energetically head-bobbing with their crest feathers erect and pumping their tails. The same territorial behaviour occurs in the more widespread White-eared Jacamar G leucotis after playback. BLACK-GIRDLED BARBET Capito dayi Fairly common at Fazenda Rancho Grande, where it was regularly seen by K. J. Zimmer and myself, often feeding in the midstorey or canopy on small berries and Cecropia catkins at terra firme edge. Possibly less common in forested areas at Paakas Palafitas, where observed on only three occasions in terra firme. Stotz et al. (1997) noted the species as being common on the middle rio Ji-Parana in terra firme, seasonally flooded forest and river-bluff forest. Foraging observations consisted of perch-gleans to leaf and branch surfaces, often on terminal branches in the subcanopy. Prey included a large katydid or mantis that was held in the bird’s claws and repeatedly jabbed with the beak before being swallowed whole. In Mato Grosso, at the rio Cristalino, I have twice observed this species (a pair and a family group) in the understorey, foraging just above the forest floor at Eciton army ant swarms, where they pursued escaping arthropods in dead fallen bamboo. CURL-CRESTED ARACARI Preroglossus beauharnaesii Fairly common in ferra firme at Paakas Palafitas, where groups were seen near- daily. However, the species was not recorded at Rancho Grande or at the two sites Andrew Whittaker 253 Bull. B.O.C. 2004 124(4) along the middle rio Ji-Parana (Stotz et al. 1997), suggesting that the species may be patchily distributed in RondO6nia and possibly is absent from some regions. WHITE WOODPECKER Melanerpes candidus Three were observed on Palafitas Island in July 2002 and, in June 2003, a vocalis- ing pair was observed flying high above Pakaas Palafitas Lodge along the rio Mamoré before landing in second growth near the lodge. The distribution of this woodpecker in Rond6nia is poorly known and these records may prove to be the first for the state. Within Amazonia the species seems very local, preferring vdrzea and mature river islands. Whereas in other parts of its range the species is found in patchy Atlantic Forest, it seems to be most abundant, in Brazil, in gallery forests of the Pantanal in Mato Grosso (pers. obs.). POINT-TAILED PALMCREEPER Berlepschia rikeri This Moriche Palm Mauritia flexuosa specialist was tape-recorded in extensive palm groves within a swampy area surrounded by cattle pasture at Paakas Palafitas Lodge. The species’ distribution in Rond6nia is very poorly known and it was not recorded by Stotz et al. (1997) at either of their study sites, although there are records from the upper rio Madeira (Pinto 1978). DUSKY-CHEEKED FOLIAGE-GLEANER Anabazenops dorsalis I tape-recorded and observed a lone individual of this bamboo specialist (Parker et al. 1997) in the understorey of terra firme at Parque Estadual de Guajara-Mirim, on 23 April 1995. This represents only the third documented locality for the species in Brazil. The others are Cachoeira Nazaré, where two specimens were collected (Stotz et al. 1997), and Alta Floresta, Mato Grosso, where it has been tape-recorded (Zimmer et al. 1997). In response to playback the bird approached closely, uttering a long series of fast chattering notes, with its white throat-feathers erect, wings partially open and drooping, and its crown feathers slightly raised. I have noted the same behaviour to playback at the rio Cristalino, Mato Grosso. GREY-THROATED LEAFTOSSER Sclerurus albigularis This forest dweller was tape-recorded and observed in terra firme at Parque Estadual de Guajara-Mirim, on 23 April 1995. K. J. Zimmer and I also made observations and tape-recordings of other individuals at Fazenda Rancho Grande in 1990-1995. The first Brazilian record was from Cachoeira Nazaré (Stotz et al. 1997) where it was described as rare, with one mist-netted in 1986. Two were recently collected at Alvorada do Oeste, Rond6énia (Whittaker & Oren 1999). These Rond6nian specimens apparently concern the subspecies albicollis (Remsen 2003) and not kempffi, which was only recently described from nearby Bolivia (Kratter 1997), as suggested by Stotz et al. (1997). Andrew Whittaker 254 Bull. B.O.C. 2004 124(4) WEDGE-BILLED WOODCREEPER Glyphorynchus spirurus inornatus Very common understorey inhabitant of terra firme at all sites. Rond6nian birds refer to the subspecies inornatus, found south of the Amazon from the right bank of the rio Madeira to the left bank of rio Tapajés, extending south to northern Mato Grosso along the rio Roosevelt. The voice of this Brazilian endemic distinctly differs from nominate birds, strongly suggesting that more than one species is involved in Glyphorynchus (Marantz et al. 2003; pers. obs.), and that a thorough revision of its taxonomy is required. The most commonly heard voice of inornatus is two loud, clear penetrating notes, TUE, TUE... repeated every 5—8 seconds, and very unlike the commonly heard ‘sneezing’ chief notes of other Amazonian taxa. The complex song of inornatus also differs, being a more musical series, rising up the scale, with a more buzzy series of terminal notes (pers. obs.). On 8 July 2002, while in terra firme at Novo Colonia I flushed an incubating Glyphorynchus from its nest in a hollow, broken vertical stump c.1.25 m high and 30 cm in diameter. The nest cup was c.1 m inside the stump and contained two small white eggs. CURVE-BILLED SCYTHEBILL Campylorhamphus procurvoides I tape-recorded and observed one in terra firme at Parque Estadual de Guajara- Mirim on 25 April 1995, presumably of the race probatus, which occurs on the south bank of the Amazon and east of the rio Madeira to the left bank of the rio Tapajos (Peters 1951). Parker et al. (1997) recorded it as rare in terra firme forests at Cachoeira Nazaré, with only two collected, which were the first records for Rondénia. The voice of Curve-billed Scythebill that I tape-recorded in Rond6nia was strikingly different from nominate procurvoides, with which I am very familiar from the north bank of the Amazon at Manaus, Amazonas. However, the Rondonian voice is identical to those I have tape-recorded at Alta Floresta, which are of the race multostriatus (Peters 1951) and is somewhat associated with bamboo. Tape- recordings I have made of sanus in southern Venezuela also distinctly differ from nominate birds and from the two south-bank forms. During extensive field work, I have found consistent and distinctly different vocal types throughout the species’ range, strongly implying that more than one species is involved. I am currently reviewing vocal data and species limits in Curve-billed Scythebill. STRIATED ANTBIRD Drymophila devillei This bamboo specialist was tape-recorded in a stand of Guadua bamboo near the rio Formoso at Parque Estadual de Guajara-Mirim, on 26 April 1995. I confirmed by plumage characters (ochraceus underparts) and vocal differences from nominate devillei that these birds represented the race subochracea. Other state records of Striated Antbird exist only from 40 km west of Cachoeira Nazaré (Parker ef al. 1997), where four specimens of the nominate race were taken in bamboo. Novaes (1976), however, reported specimens of subochracea from the nearby rio Aripuana, Andrew Whittaker 255 Bull. B.O.C. 2004 124(4) and I recently confirmed the presence of this subspecies along its major tributary, the rio Roosevelt. Only subochracea has been found at Alta Floresta (Zimmer et al. 1997). Parker et al. (1997) noted that the distance between Cachoeira Nazaré and rio Aripuana is less than 250 km, with no apparent geographical barrier between them. These new records of subochracea confirm that both races occur south of the rio Ji-Parana, with no major river barriers between the sites, and provide even stronger evidence of the theory that more than one species is involved (Zimmer & Isler 2003; pers. obs.). Documented site records for Brazil are very few and scattered, thus any new documentation sheds light onto its Brazilian range. In 1992, I recorded a significant range extension for the species near the lower rio Jurua, along the Amazon at Caitau-uara, where I tape-recorded and observed nominate devillei in Guadua bamboo. I had previously collected the same taxon from the headwaters of the upper rio Jurua (Whittaker & Oren 1999). Almost nothing is known of the species’ breeding biology, except for a single report of a female entering an apparent domed nest in bamboo (Zimmer & Isler 2003). I observed a pair feeding a full-grown juvenile (in female plumage) at Parque Estadual de Guajara-Mirim on 27 April 1995. THRUSH-LIKE ANTPITTA Myrmothera campanisona subcanescens K. J. Zimmer and I noted, at Fazenda Rancho Grande in 1991, that the loudsong of this form is distinctly different from all other subspecies. Further extensive tape- recordings made by us throughout the range of M. campanisoma, including all of the Brazilian subspecies, convinced us that subcanescens exhibits consistent vocal differences both in loudsong and calls. We are currently examining vocal variation within the entire M. campanisona complex, with an eye toward possibly revising species limits. The race subcanescens is a Brazilian endemic found only south of the Amazon, east of the rio Madeira to the right bank of the rio Tapajos. GREENISH ELAENIA Myiopagis viridicata Fairly common in terra firme near Paakas Palafitas Lodge both in July 2002 and June 2003, when I tape-recorded and observed several individuals. The species typically inhabits gallery forest during the breeding season, so these records in ferra firme outside the breeding season concern austral migrants. Stotz et al. (1997) recorded it as an uncommon austral migrant in low forest and second growth at Cachoeira Nazaré. The species is only a winter visitor to Peru and the states of Acre and Rond6nia in north-west Brazil (Chesser 1995). Much further east it has been recorded at Alta Floresta, Mato Grosso, also in terra firme forest, in August (Zimmer et al. 1997), where it is a presumed austral migrant. LARGE ELAENIA Elaenia spectabilis Common on Palafitas Island with multiple individuals in July 2002 and June 2003. Chesser (1997) reported it as an austral migrant in Bolivia north of c.18°S and | Andrew Whittaker 256 Bull. B.O.C. 2004 124(4) recorded Large Elaenia as a common migrant breeder in cerrado, around Cuiaba, Mato Grosso, in September. However, in June and late-July visits I have found these areas completely lacking the species. These presumed austral migrants were vocal, with the commonly heard single call note being tape-recorded (also heard on the breeding grounds; pers. obs.). I noted several hover-gleaning and feeding on Cecropia catkins on the river islands, Where agonistic behaviour was also observed, suggesting territoriality on the wintering grounds. I have noted the species to be a fairly common austral visitor to successional vegetation on river islands in the Amazon and its major tributaries (pers. obs.). PLAIN TYRANNULET J/nezia inornata This small tyrant flycatcher was fairly common, with multiple birds seen daily, at Guajara-Mirim in July 2002 and June 2003. Here I found the species in various habitats including on Palafitas Island, in igapd, second growth along the rio Mamoré and in oxbow lake vegetation. However, one was found at the edge of a small manioc field, uncharacteristically foraging 25-m high in the subcanopy of terra firme. Birds were rather vocal, regularly giving a long, very piculet Picumnus- like trill; this voice is very different from the more musical one heard in northern Argentina on the breeding grounds (pers. obs.). I have also noted this piculet-like voice commonly in the northern Pantanal, Mato Grosso, during the austral winter. Plain Tyrannulet is a known austral migrant to south-west Amazonia, with previous specimens from Rond6nia (Stotz et al. 1997). I believe these records refer to austral migrants, which were considered to be common in low forest at Cachoeira Nazaré in May—July by Stotz et al. (1997). The species is also known from the Brazilian Amazon in Acre (Chesser 1995), with unpublished observations from the upper rio Jurua in the austral winter (pers. obs). It is also reported to occur in southern Amazonian Peru (Parker et al. 1982) and adjacent northern Bolivia (Gyldenstolpe 1945). Chesser (1997) listed it as a winter resident at Pando, El Beni and in northern dpto. Santa Cruz, above c.17°S. SUBTROPICAL DORADITO Pseudocolopteryx acutipennis My observations are the first Brazilian records and certainly refer to austral migrants. All records were from Palafitas Island in the rio Mamoré. A single observed at close range on 4 July 2002 had the distinctly bicoloured bill, black on the upper mandible and pink on the lower, indicative of an immature (Ridgely & Tudor 1994). A presumed second individual, also an immature, was observed shortly afterwards, 250 m away in another part of the island. A third record involved a lone bird, on 10 July 2002, c.1.5 km from the original site, and this bird was documented with video footage. It had an all-dark bill and was a presumed adult. On 21 June 2003, again on Palafitas Island, a doradito, presumably Subtropical, was briefly seen by S. L. Hilty and myself. Andrew Whittaker 257 Bull. B.O.C. 2004 124(4) Prolonged close studies of these three birds, for a total of c.11 minutes, allowed for excellent field studies. All had two pale creamy-white wingbars and a dark smudge on the cheeks, forming a darker patch that was most notable at close range. No contrast in head to back colour was noted, with a uniform olive crown, back and wings. At close range | noted the first immature as having dark eyes and blue-grey legs. The birds were inquisitive, in response to ‘pishing’ approaching closer in the tall cane grass, which was abundant on the island and in which they were most frequently observed. Here they regularly clung to vertical stems and occasionally perched on larger horizontal leaves at c.12—36 cm, sallying into the dense cane grass before reappearing minutes later and often at some distance. I observed both wing- and tail-flicking, especially when the birds were agitated or nervous. One was observed moving through a recently burnt area with 1.5 m burnt canebrake and young Cecropia, climbing to 3.5 m in a burnt tree before dropping to forage in low semi-burnt canebrake. Subtropical Doradito breeds locally in the Andes from northern Colombia to north-west Argentina, spreading into adjacent lowlands during the austral winter (Ridgely & Greenfield 2001). Chesser (1997) noted that in Bolivia during the breeding season the species is found at 2,200—3,550 m, but in the austral winter it reaches the adjacent departments of Santa Cruz, Cochabamba, El Beni and La Paz, where the species occurs in May—June, August, October and December, but never above 700 m. I suggest that the species is easily overlooked especially as it is not vocal during the austral winter. Through more ornithological field work in the state at this season, Subtropical Doradito may prove to be a fairly regular visitor to Rond6énia and possibly other parts of western Amazonian Brazil. YELLOW TYRANNULET Capsiempis flaveola Several pairs were observed and tape-recorded in 2002 and 2003, at the margins of the oxbow lake at Pacaas Palafitas Lodge, where they only associated with dense stands of an unknown genus of small-leaf bamboo. An extensive area of bamboo, covering several km on the left bank of the rio Paakas Novos (following extensive deforestation), also held the species, where it was common. This active little tyrant shared such habitat with Stripe-necked Tody-tyrant Hemitriccus striaticollis. These records represent a range extension within Brazil from the nearest known records 600 km to the west at Alta Floresta (Zimmer et al. 1997), and seem to be the first documented for the state. Yellow Tyrannulet seems to be very patchily distributed through much of Amazonia, with documented records south of the Amazon and west of the rio Madeira practically non-existent. I have collected specimens south of the Amazon at Caitau-Uara, Amazonas, in September 1992 (housed in the Museu Emilio Goeldi, Belém). These also seem to be the first documented from the rio Purtis/rio Jurua interfluvium. Specimens are also known from the west bank of the rio Madeira, 60 km south-west of its confluence with the Amazon. Pacheco (1995) reported a Andrew Whittaker 258 Bull. B.O.C. 2004 124(4) westward range extension involving a small population at Mamiraua, Amazonas, on the north bank of the Amazon. SOUTHERN SCRUB FLYCATCHER Sublegatus modestus Singles of this rather easily overlooked nondescript flycatcher were noted on four visits to Palafitas Island in July 2002 and once in June 2003. I closely observed and tape-recorded the single rising whistled note. Field identification was based on their brighter overall appearance, more contrasting underparts and bolder pale wingbars, versus the very similar but duller Amazonian Scrub Flycatcher S. obscurior. In Amazonia, Amazonian Scrub Flycatcher seems to be found strictly in upland tropical forest, where it inhabits open canopy, large treefall clearings, natural or man-modified forest edge, and in vdrzea on floodplains close to major rivers where dense Guadua bamboo occurs in the understorey (pers. obs.). Southern populations (brevirostris) are at least partially migratory with winter records from Amazonian Peru, in Ucayali and Madre de Dios (Ridgely & Tudor 1994). Stotz et al. (1997) reported S. modestus as a rare austral migrant in second growth at Cachoeira Nazaré, and it was found during the austral winter in Bolivia north of 17°S, in June—September (Chesser 1997). During the austral winter I have observed migrant modestus in large stands of Guadua bamboo in Manu National Park, Madre de Dios, Peru, in river floodplains within vdrzea. Here, during the austral winter, I have found modestus to be syntopic with resident Amazonian Scrub Flycatcher, which was once considered a subspecies of modestus (Traylor 1982). ZIMMER’S TODY-TYRANT Aemitriccus minimus This easily overlooked tyrant flycatcher was located by its distinctive voice, and tape-recorded and observed at the Taquaras campina forest, where two territorial birds were noted in July 2002 and June 2003. Singing in the higher forest substrate, its insect-like vocalisation is easily overlooked until known. This behaviour, combined with it inhabiting mostly forest canopy and subcanopy (only rarely coming lower), confirms why the species mostly is under-recorded. Now that field ornithologists are familiar with the voice, its known range has been greatly expanded (Zimmer et al. 1997, Cohn-Haft 2000, Borges et al. 2001). I have tape- recorded the species in Mato Grosso, at Fazenda Esperanca (near Bom Jesus de Araguaia) and at Xingu Refugio Amazonica, the rio Von Den Steinen, and K. J. Zimmer and I also tape-recorded it at Borba, in Amazonas, at Amazonia National Park, Caxiuana and Carajas, all in Para, and at Caseara, in Tocantins. The latter record is the first documentation of the species east of the rio Tocantins. BUFF-CHEEKED TODY-FLY CATCHER Todirostrum senex Despite being considered ‘unknown in life’ (Ridgely & Tudor 1994), I was able to identify the species based on familiarity with its vocalisations and appearance acquired at the type locality, where M. Cohn-Haft and B. M. Whitney (pers. comm.) Andrew Whittaker 259 Bull. B.O.C. 2004 124(4) rediscovered it several years ago. They kindly alerted me to its presence and are currently preparing a paper concerning its natural history and taxonomic affinities. On 12 July 2002 I located this little-known species at Taquaras by virtue of its distinctive voice (a rather loud, dry metallic trill) in dense stunted campina-type forest. Here I observed and tape-recorded several individuals, initially in July 2002 and again on 25 June 2003. This campina is on white sand and weathered clay that is poorly drained. I also found Zimmer’s Tody-tyrant Hemitriccus minimus sympatric with Buff-cheeked Tody-flycatcher. Zimmer’s Tody-tyrant mostly foraged in the higher forest substrate, whilst vocally Buff-cheeked Tody-flycatcher was the commoner of the two. Even though July is the dry season here, the stunted campina had several small pools and muddy areas, and in June 2003 was even wetter, confirming that the area is flooded during the wet season (November—April). The canopy was fairly uniform in height (8-12 m), with low tree species diversity, dominated by 1.25—2.5-m Melastoma spp. in the understorey, with some of the forest floor covered by moss and low terrestrial bromeliads. Following playback, two T. senex permitted approach to 3-4 m while they foraged in the fairly open understorey. They spent long periods foraging in Melastoma at 1-2 m, but also in lower branches of trees up to 4-5 m. Audible wing- whirr was very noticeable as they flew between perches and could be heard at 15-20 m. I noted short sally-gleans of 0.5—2.0 m to live leaves and occasionally to branches or trunks, and a 5-m diagonal sally was observed. The only identified prey was a l-cm green Orthoptera, which was held in the beak and bashed repeatedly against a branch before being swallowed whole. These records, along with unpublished observations by M. Cohn-Haft and B. M. Whitney (pers. comm.) from further north in Rond6nia, are the first state records. My records represent a range extension of c.850 km south-southwest of Borba, the type locality. I have also recently tape-recorded the species along the lower rio Roosevelt, at Pousada Rio Roosevelt, Amazonas (08°29’S, 60°57’W), extending the known range further east. Whether the Rond6nian or rio Roosevelt birds represent disjunct populations or whether the species is continuously distributed over this region, perhaps even in suitable habitat in adjacent Bolivia, requires further field and museum work. Recent field work in white-sand areas has resulted in several noteworthy ornithological discoveries, including new taxa and rediscoveries (Whittaker 1994, Whitney & Alvarez Alonso 1998, Isler et al. 2001), re-emphasising the exceptional conservation importance of these unique forests. Alarmingly, from July 2002 to June 2003, subsistence farmers at Taquaras cleared several pristine areas of campina holding T: senex. Unfortunately, the ever-increasing human population of the area and the economic value of white-sand soil for the building construction trade, combined with subsistence farming, are now threatening this habitat before it has been biologically surveyed, much less protected. Andrew Whittaker 260 Bull. B.O.C. 2004 124(4) FUSCOUS FLYCATCHER Cnemotriccus fuscatus Very common and vocal around Paakas Palafitas on both visits, in terra firme clearings and along roads lined with bamboo through terra firme, second growth, varzea edge, river islands and igapo. Apparently a fairly common austral migrant to western RondOnia, residents in Amazonia occur only in early-successional vegetation on river islands (pers. obs). Stotz et al. (1997) recorded the species as a rare austral migrant at Cachoeira Nazaré, in lowland forest. EULER’S FLYCATCHER Lathrotriccus euleri Presumed austral migrants were uncommon and not very vocal in second growth bordering terra firme and igapo around Paakas Palafitas Lodge, in July 2002 and (rare) in June 2003. Interestingly, Euler’s Flycatcher was found to be absent from the middle rio Ji-Parana sites a little further north (Stotz et al. 1997). OLIVE-SIDED FLYCATCHER Contopus borealis This boreal migrant was observed at Rancho Grande on 29 and 31 January 1993, 24 January and 3 November 1995. All records were from the terra firme/second- growth ecotone, where they perched high in the canopy (mostly on dead snags). These are perhaps the first records for Rond6nia, although scattered records are available from elsewhere in Amazonia (Cohn-Haft et al. 1997), and I have unpublished records from Alta Floresta (Mato Grosso) and the Serra dos Carajas (Para). VERMILION FLYCATCHER Pyrocephalus rubinus Around Paakas Palafitas Lodge this distinctive tyrant flycatcher was very common in June 2003 and uncommon in July 2002. Several males were recorded in heavy body and tail moult. This species is an austral migrant, inhabiting terra firme edge, river islands and cattle pasture. Reported as a winter visitor to most of Bolivia except the extreme south (Chesser 1997). At Cachoeira Nazaré it is a rare austral migrant in second growth (Stotz et al. 1997). LITTLE GROUND-TYRANT Muscisaxicola fluviatilis This species’ range in Brazil is very poorly known, with only two historical specimens—from Crato (just north of Humaita), on the left bank of the rio Madeira, Amazonas, on 14 November 1829 (Pelzeln 1870); and at Milho, on the rio Jiparana (c.150 km south-east of its mouth), Rond6nia, on 19 June 1908 (Hellmayr 1910)— and several recent sight records. I recorded it as fairly common at Palafitas Island, in July 2002, where 3-4 were seen, mostly on sandbars, exposed mudbanks and occasionally in low scrubby successional vegetation close to the river’s edge. However, in June 2003 only one was found. Stotz et al. (1997) reported the species as rare at Cachoeira Nazaré and other reports come from observations by P. Roth along the upper rio Aripuana, Mato Grosso in August—October (Pacheco 1994). Recent sightings from Amazonas include singles near Tefé, on 1 July 1993, and 30 Andrew Whittaker 261 Bull. B.O.C. 2004 124(4) km west of the lower rio Japura, on 15 July 1993 (Pacheco 1994). I have unpublished records of several individuals along the upper rio Jurua, at Eirunepé, on 10 October 1991. Interestingly, all these records fall within the period of austral migration. Sick (1993) suggested that the species might appear in Brazil only during migration. HUDSON’S BLACK-TYRANT Knipolegus hudsoni On 20 June 2003, on Palafitas Island, | observed an adult male, and the following day S. L. Hilty and I observed both an adult male and female-plumaged bird. The adult male was territorial, repeatedly chasing the female-plumaged bird through low Tessaria scrub. However, males possess a female-type plumage following post- juvenile moult (Fjeldsa & Krabbe 1990), and thus females cannot certainly be separated from young males in the austral winter. This species is an austral migrant to Brazil, previously recorded only from Mato Grosso, at Descalvados, in the Serra do Roncador in August-September (Sick 1985). It breeds in chaco woodland in central Argentina, from Cordoba south to Rio Negro and south-west Buenos Aires provinces. Austral migrants are also known from nearby Bolivia, with a few records from Paraguay (Hayes 1995). Formerly considered Near Threatened (Collar et al. 1992), I believe these river island observations are important, as they confirm yet another habitat for the species on its wintering grounds. During the austral winter, migrants have been reported from trees and bushes at woodland and road edges in Beni, Bolivia (Brace et al. 1996), and from Santa Cruz in chaco, weedy pasture and even gardens (Parker 1989). S. L. Hilty and I have recorded it in hedges, overgrown pasture and near windbreaks by sewage ponds in Santa Cruz. BLACK-BACKED WATER-TYRANT Fluvicola albiventer One observed on 11 July 2002 on Palafitas Island was feeding at the water’s edge on exposed mudbanks. Recorded as a winter resident in Bolivia, from adjacent Santa Cruz and El Beni in June—November (Chesser 1997), and Peru (Parker et al. 1994), in Brazil it is an austral migrant to Acre, Rond6nia (Chesser 1995) and south-east Mato Grosso (Willis & Oniki 1990). RUFOUS CASIORNIS Casiornis rufa Three records of this austral migrant: one observed and tape-recorded in the canopy of terra firme on the edge of a man-made clearing near Paakas Palafitas Lodge on 9 July 2002; a second heard in the canopy of igapé at Nova Colonia on 10 July 2002; and the last, a silent individual, in the Taquaras campina forest on 26 June 2003. Reported in low forest from the middle rio Jiparana at Cachoeira Nazaré, where specimens were obtained in May and June (Stotz et al. 1997). Other Brazilian Amazon records (north of the Amazon) are from northern Para (Snethlage 1914) and in gallery forest c.50 km south of Porto Grande, Amapa (K. J. Zimmer, pers. comm.). South of the Amazon in Brazil the species is known from Acre (Stotz Andrew Whittaker 262 Bull. B.O.C. 2004 124(4) et al. 1997) and Alta Floresta, northern Mato Grosso, in September, in isolated small deciduous forests on rocky outcrops within terra firme (Zimmer et al. 1997). PALE-BELLIED MOURNER Rhytipterna immunda At Taquaras campina 2-3 of this easily overlooked species were located in low, stunted and poorly drained sandy/clay forest by virtue of their distinctive voice, which was tape-recorded. Their resemblance to Myiarchus flycatchers, as already reported (Ridgely & Tudor 1994, Zimmer & Hilty 1997), is striking. In response to playback, they were rather shy and retiring, flying to the canopy of 8—10-m trees, where they briefly perched very alert before quickly retreating from sight. These documented records seemingly are the first for Rond6nia. Known from specimens in the Museu Emilio Goeldi (Belém) taken in campina near Borba further down the rio Madeira, the nearest Brazilian records are from southern Mato Grosso (Ridgely & Tudor 1994). BROWN-CRESTED FLYCATCHER Myiarchus tyrannulus Remarkably common austral migrant with multiple birds recorded daily, although far more often heard than seen, as found mostly high in the canopy of terra firme. Also recorded in the canopy of varzea on mature river islands and along wooded banks of the rio Mamoré. Apparently present only in winter (June—October) in adjacent northern Bolivia (Chesser 1997). At Cachoeira Nazaré presumed austral migrants were recorded twice in low forest in June. At other Amazonian sites in Brazil, known from specimens taken in the austral winter in Acre and Rondonia (Chesser 1997) and at Alta Floresta, Mato Grosso, in August-September (Zimmer et al. 1997). However, there are isolated resident breeding populations in Amazonian savannas, at Alta do Chao, Para (Sanaiotti & Cintra 2001) and the lower rio Xingu, including Parque Indigena do Xingu (pers. obs.). The complete lack of other published records outside the austral winter from most of the Amazon basin confirms that the species is almost exclusively an austral visitor to the Brazilian Amazon and that it is commoner in south-west Amazonia. YELLOW-THROATED FLYCATCHER Conopias parva This canopy flycatcher was very uncommon at Nova Colonia, on 8 July 2002, and was observed and tape-recorded at Taquaras campina, on 12 July 2002, where it was found accompanying a small mixed-species flock. The record from Nova Colonia, in south-west Rond6nia, quite probably represents the species’ southern- most locality. The species’ canopy habits, where it occurs exclusively in the upper strata mostly of terra firme, make it especially prone to be overlooked (Whittaker & Oren 1999, Alvarez Alonso & Whitney 2003), unless its distinctive voice is known (pers. obs.). Until recently, this has caused large gaps and poor representation of its true range in the literature, especially south of the Amazon (Ridgely & Tudor 1994). Brazilian records south of the Amazon are one from Urucu, Amazonas (Peres & Andrew Whittaker 263 Bull. B.O.C. 2004 124(4) Whittaker 1991) and the upper rio Jurua, Acre (Whittaker & Oren 1999), the latter overlooked by Alvarez Alonso & Whitney (2003). However, Alvarez Alonso & Whitney (2003) reported a series of new observations by B. M. Whitney south of the Amazon in Brazil, from the west bank of the lower rio Tapajés west to extreme western Acre, and south along both banks of the rio Madeira in northern Rondonia. I also have voucher tape-recordings documenting Yellow-throated Flycatcher south of the Amazon, from Amazonas along the rio Mapia, near Borba, and in the extreme west of the state on the Peruvian border, along the rio Javari, at Palmari Lodge, in August 2002. Recent north-bank records from west of the rio Negro are available from Jau National Park (Borges et al. 2001). I also have tape documentation both north and south of Jai National Park, with a pair c.35 km east of Manacapuru, Ziggylandia, and a nesting pair tape-recorded and observed at Barcelos, Amazonas, on 20 December 1997. This pair was seen carrying nest material to a hollow 20 m up in an isolated tree, in second growth some 100 m from virgin terra firme. I found Yellow-throated Flycatcher and Three-striped Flycatcher Conopias trivirgata together at Ziggylandia, Amazonas, where I have observed both in the canopy of terra firme, but never in the same canopy flock. Possibly C. trivirgata is more restricted, in these areas, to black-water transition (only occasionally ventur- ing into terra firme), which borders terra firme, and C. parva is exclusively restricted to upland terra firme. Increased field work by ornithologists familiar with Yellow-throated Flycatcher’s voice will surely bring greater insight into its precise Amazonian range. However, the reported absence in Rond6nia from both the middle rio Ji- Parana (Stotz et al. 1997), and Rancho Grande, where experienced field workers familiar with its voice have failed to find it, suggests that the species is rather local and patchily distributed east of the rio Madeira. The species’ patchy distribution was also noted by Alvarez Alonso & Whitney (2003), who suggested that it occurs only in forests on sandy and other nutrient-poor soils. YELLOW-BROWED TYRANT Satrapa icterophrys One observed by S. L. Hilty and I on Palafitas Island, on 20 June 2003, in early- successional growth including Jessaria and canebrake, seemingly represents the first state record and presumably was an austral migrant. Chesser (1997) reported Yellow-browed Tyrant as an austral migrant (June—October) to northern Bolivia. Amazonian records are few, although Ridgely & Tudor (1994) reported it to be less numerous further north, where it apparently occurs only as an austral migrant, noting one record from Manaus, Amazonas. This record involved a bird I observed nest building at Machantaria Island, in the Amazon, on 30 August 1992. Subsequent visits, over several years by various ornithologists, failed to produce any further records on this or other nearby river islands. I therefore suggest this breeding record to have been exceptional. In the northern Pantanal, Mato Grosso, it is a not uncommon austral migrant (pers. obs.). Andrew Whittaker 264 Bull. B.O.C. 2004 124(4) BLACK-NECKED RED-COTINGA Phoenicircus nigricollis Two observed and tape-recorded by S. L. Hilty and myself in terra firme near Paakas Palafitas Lodge, on 23 June 2003, was the second state record, following the report of one observed and tape-recorded at Parque Estadual de Guajara-Mirim, in April 1995 (Whittaker 1996a). It seems highly probable that the species also occurs in adjacent north-east Bolivia. BLACK MANAKIN Xenopipo atronitens This sandy soil specialist was fairly common in the Taquaras campina, where several adult males and female-plumaged birds were observed and tape-recorded. This seems to be the first state record, with the nearest known populations being in north-east Bolivia, in Santa Cruz, on the Serrania de Huanchaca (Ridgely & Tudor 1994). In Brazil the nearest site for Xenopipo is in south-west Mato Grosso (Ridgely & Tudor 1994). My record represents a range extension within the Madeira drainage of c.850 km from Borba, from where there are specimen records (Pinto 1944). SOUTHERN ROUGH-WINGED SWALLOW Stelgidopteryx ruficollis Presumed austral migrants involved flocks of 50+ along the rio Mamoré, in July 2002, swelling local residents, which almost never flock (pers. obs.). However, no large numbers were noted in June 2003. Southern populations are migratory, moving north in Brazil (Pereyra 1969), with birds from Rio Grande do Sul largely absent in mid February to mid August (Belton 1985). I have also observed larger numbers of the species, with flocks of over 100, along several major Amazonian rivers in the austral winter (pers. obs.). However, the full extent of their winter range in the Amazon is unclear and difficult to document due to the species being a common resident throughout the region. TOOTH-BILLED WREN Odontorchilus cinereus This canopy species was observed and tape-recorded near Paakas Palafitas Lodge in mixed-species canopy flocks in terra firme, where it was fairly common and very vocal, especially in June 2003. R. S. Ridgely, K. J. Zimmer and I found it very common at Fazenda Rancho Grande, where on 25 April 1991 a pair was observed carrying twigs to a nest cavity 20 m high at the edge of terra firme. The pair was also seen in courtship display and any other birds approaching the nest were chased aggressively. Stotz et al. (1997) reported the species as common at Cachoeira Nazaré and uncommon at Pedra Branca. At Alta Floresta, Mato Grosso, Zimmer et al. (1997) reported it to be uncommon. The species also occurs in adjacent north- east dpto. Santa Cruz, Bolivia (Bates et al. 1989, 1992). CREAMY-BELLIED THRUSH Turdus amaurochalinus Austral migrants to Rond6nia were recorded as rather uncommon around Paakas Palafitas, mostly in second growth and terra firme edge. Further north, it was absent Andrew Whittaker 265 Bull. B.O.C. 2004 124(4) at Pedra Branca and uncommon at Cachoeira Nazaré (Stotz et al. 1997). However, the species is mostly absent or very rare east of here in Amazonia (pers. obs.). Recorded as common 700 km to the south-east, where up to 10,000+ roost annually in the bamboo understorey of terra firme at Flor del Ouro, Noel Kempff Mercado National Park, Santa Cruz, Bolivia, in July (S. L. Hilty & A. Whittaker pers. obs.). PEARLY-BREASTED CONEBILL Conirostrum margaritae I initially observed an adult feeding an immature in low Cecropia on a Bolivian river island adjacent to Palafitas Island, in the rio Mamoré, on 11 July 2002. In June 2003, S. L. Hilty and I documented this new record for Bolivia when we tape- recorded and observed several small groups on the same island in Cecropia-dominated stands of trees. I also observed and tape-recorded a pair of Chestnut-vented Conebills C. speciosum in the same Cecropia stand. On the Amazon, near Manaus, at Machantaria Island, Amazonas, I have recorded Pearly- breasted, Chestnut-vented and Bicoloured Conebills C. bicolor, which might represent the first documentation of these conebills occurring syntopically. The most commonly heard voice is a complex series of fast musical twittering notes, which sounds as if several birds are singing concurrently, but often involves only a single bird singing within a small group. I have found the species to always be very responsive to playback. This appears to represent the first record for Bolivia. Previously, C. margaritae was known only from the lower rio Madeira near Borba (Peters 1968), where I observed it in 2001. Known elsewhere in Brazil from along the middle Amazon, from the mouth of the rio Jamunda to the mouth of the rio Negro (Ridgely & Tudor 1989), the Bolivian records represent a range extension of c.1,050 km. Pearly- breasted Conebill probably has a continuous range along the entire Amazon in Brazil, a supposition supported by my tape-recordings and specimens from Caitau- Uara, in September 1992, which extended the range some 600 km west. SLATE-COLOURED SEEDEATER Sporophila schistacea Several singing adult males and immature males (in female plumage) were tape- recorded, and small loose flocks of 5—8 were observed, at Paakas Palafitas in June 2003. They were associated with small agricultural clearings in terra firme, especially where dry-land rice was being cultivated. Two or three were also observed at Parque Estadual Guajara-Mirim in forest borders close to small patches of bamboo and overgrown cattle pasture. An adult male tape-recorded singing on 27 January 1995 at Rancho Grande was the only record for the site; it frequented a recently burned forest edge bordering grassland. At Paakas Palafitas males were observed singing mostly from concealed perches at the forest edge, usually at 4-8 m, but reaching 11—12 m after playback. Singing birds were very territorial, being extremely responsive to playback and affording excellent close studies. The large yellow bill was very obvious on adult males, which showed pink gapes when singing. Other field marks noted on this Andrew Whittaker 266 Bull. B.O.C. 2004 124(4) basically grey bird were the two small symmetrical white spots on the lower neck and darker grey centre to the throat, with a white mid belly. Previously recorded in Rond6nia only from Cachoeira Nazaré, where it was reported as rare (only two March records) and fairly common at nearby Pedra Branca in terra firme and secondary forest, in February (Stotz et al. 1997). Stotz et al. (1997) suggested the species might be nomadic, as found by Parker et al. (1982) in south-east Peru. In Costa Rica, Willis & Eisenmann (1979) and Stiles & Skutch (1989) noted that Slate-coloured Seedeater is possibly an irruptive species follow- ing bamboo seeding, as in Panama. However, my observations, and those of Stotz et al. (1997) in RondOnia, confirm that the species also occurs in areas lacking bamboo, as at two of the sites where I located it bamboo was absent. In Acre, west Amazonian Brazil, Whittaker & Oren (1999) found the species to be only associ- ated with bamboo. Recent deforestation in Rond6énia and elsewhere in the Amazon has resulted in the cultivation of dry rice in small agricultural settlements, which seems to be a very important alternative food resource for the species (pers. obs.). Stotz et al. (1997) noted that stomach contents of nine specimens taken at Pedra Branca contained rice, which was being harvested. This newly available food, combined with increasing bamboo as a result of the creation of forest gaps (Janzen 1983, Marcus 1983), may lead to an increasing and more widespread population of the species within Amazonia. DARK-THROATED SEEDEATER Sporophila ruficollis S. L. Hilty and I observed an adult male at Palafitas Island on 20 June 2003, along with three unidentified female seedeaters. In Brazil known previously only from Mato Grosso, Goids, S40 Paulo and in Minas Gerais, at Pirapora in September (Sick 1985). This is apparently the first state record and confirmation that the species occurs on river islands in early-successional growth. Significant numbers have been recorded in Bolivia at Noel Kempff Mercado National Park, some 700 km to the south-east, with estimated numbers reaching 16,160 (Pearce-Higgins 1996). RUFOUS-RUMPED SEEDEATER Sporophila hypochroma S. L. Hilty and I observed an adult male of this Near-Threatened species on Palafitas Island on 19 June 2003. It was perched atop a 6-m Tessaria in sunlight, and its calls were tape-recorded. This bird was in an area of early-successional vegetation with much seeding grass and sedges. For comparison, we recorded at least three other species of unidentified female-plumages seedeaters associated with several adult male Chestnut-bellied Seedeaters S. castaneiventris. The few documented records of this rare species in Brazil are from the southern Pantanal, east of Corumba, Mato Grosso do Sul, at Emas National Park, Goias, in October 1979, and south-west Goids, in October 1984 (Ridgely & Tudor 1989). I photographed an adult male in the northern Pantanal, at Pixiam, Mato Grosso, on 4 November 1996, in flooded grassland bordering a small marsh. Ridgely & Tudor Andrew Whittaker 267 Bull. B.O.C. 2004 124(4) (1989) suggested that the species might be an austral migrant. The Rond6nia record confirms that the species certainly wanders further north in the austral winter, but to what extent and how important river islands are to this species at this season 1s unknown. It also represents a new state record and a significant extension of its known range. The species is, however, known to be a regular austral migrant c.700 km south-east in Noel Kempff Mercado National Park, Bolivia, where estimates of 4.480 individuals were reported in August-September 1994 (Pearce-Higgins 1996). YELLOW-SHOULDERED GROSBEAK Parkerthraustes humeralis Fairly common in mixed-species canopy flocks at Fazenda Rancho Grande. Reported as uncommon at Cachoeira Nazaré (Stotz et al. 1997). On 25 April 1990, at Fazenda Rancho Grande, I observed two in the canopy of ferra firme in the bare crown of an emergent, with sluggish movements, sallying 1-3 m after a hatch of winged termites or ants. To my knowledge there are no known breeding records of the species. Whilst observing a pair in the upper midstorey of terra firme at Parque Estadual de Guajara-Mirim, on 24 April 1995, I noted one carrying a c.3.5 cm-long green leaf to the crown of a 35-40-m emergent. Two further nesting records are from Alta Floresta, Mato Grosso: in early May 2003, A. Lees (pers. comm.) observed one carrying nesting material in the canopy, and on 29 June 2003 A. Kirschel (pers. comm.) watched a pair repeatedly carrying large green leaves to the crown of a 50- m emergent in ferra firme. The most frequently heard vocalisation is a high-pitched two-syllable note (easily overlooked), the second note rising in pitch, repeated every 3—7 seconds, often from an exposed forest canopy perch. In response to playback from canopy towers, I have observed birds puff out their plumage, cock the tail almost vertically and hold it there, while flicking their wings and exposing their striking yellow shoulders (which are normally partially concealed). Maintaining this odd stance, birds often sang a more complex series of musical twittering notes (similar to the song of Palm Tanager Thraupis palmarum). | have also tape-recorded this complex voice, without playback, in the canopy of terra firme in early December at the rio Cristalino, Mato Grosso. Remarks The results of this survey augment the growing pool of knowledge concerning Rond6nia avifauna, but most of the state is still ornithologically extremely poorly known (Oren & Albuquerque 1991). The recent discovery of a new primate in the state (Ferrari & Lopes 1992) further emphasises the necessity of further field work. The results of my preliminary ornithological surveys again underline how little is known of the state’s avifauna and how much remains to be discovered. Initial surveys of a white-sand forest campina in Rond6nia have discovered the poorly known Buff-cheeked Tody-flycatcher and several other specialists of this habitat Andrew Whittaker 268 Bull. B.O.C. 2004 124(4) not previously recorded in the state. Soil mosaics within the Amazon basin are complex and dramatically modify vegetation types (Gentry 1988), which in turn have a major effect on the fauna and play an important role in defining species distributions throughout the Amazon (Gentry 1990). These results emphasise not only the importance of these campina and campinarana forests for endemic and poorly known birds, but also how fragile they are to human disturbance. Rond6nia’s ever-increasing population and expansion into untouched natural areas of the state requires immediate attention from conser- vation organisations or the future of its rich biodiversity and endemic fauna and flora may prove very bleak. A major inventory of plants and animals and their ecological requirements is urgently required throughout Rond6nia, encompassing all of the major biomes, to establish priority areas for future conservation. Acknowledgements I dedicate this paper to the memory of my father, Victor Nuttall Whittaker, who introduced me to the wonders of the natural world, especially birds. He constantly encouraged and helped me learn more about birds through his own self-taught knowledge. Unselfishly giving up his free time to drive me to bird ringing meetings, he also enrolled us both on ornithology night classes for two years, with me the youngest in the class by far. This decision was a crucial one, allowing me to mature as an ornithologist. Many of my most memorable childhood moments were birding with my father and mother in the UK, and on night class outings and family holidays in Europe. He is greatly missed. I thank my friends and colleagues Kevin Zimmer, Steve Hilty, Robert Ridgely and Guy Tudor for their companionship and help in the field during some of these surveys. The manuscript benefited great- ly from early reviews by Mario Cohn-Haft, Kevin Zimmer and Guy Kirwan, to whom I am grateful. For the excellent map I thank Mort Isler. For my travel opportunities, enabling a great part of this research, special thanks to Victor Emanuel, of Victor Emanuel Nature Tours, and Renato Cintra. 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B.O.C. 2004 124(4) Age- and sex-differentiated plumages in the two colour morphs of the Variable Buzzard Buteo polyosoma: a case of delayed maturation with subadult males disguised in definitive adult female plumage by Fosé Cabot & Tytte de Vries Received 15 September 2003 The polymorphic plumage of Variable Buzzard Buteo polyosoma has generated a long and complicated controversy regarding the species’ taxonomic classification (Vaurie 1962). Initially described as Falco polyosoma Quoy et Gaimard 1824, it has subsequently been referred to variously as Haliaeetus erythronotus King 1827; Aquila braccata Meyen 1834; Buteo varius Gould 1937; Buteo unicolor Lafresnaye & d’Orbigny, 1837; Buteo erythronotus Taczanowski, 1877; Buteo tricolor d’Orbigny (p.106 in Hellmayr 1932); Buteo melanosthetus (os) Philippi, 1899; Buteo poecilogaster Philippi, 1899; Buteo macronynchus Philippi, 1899; Buteo ater Philippi, 1899; Buteo pictus Philippi, 1899; Buteo aethiops Philippi, 1899; and Asturina aethiops Philippi, 1899. The number of synonyms is due, in part, to the fact that different plumage patterns were thought to represent different species. Since Gurney’s (1879) description of Buteo poecilochrous, a long debate has ensued as to the species’ relationship with B. polyosoma. This is to some extent understandable since several plumages of these taxa are virtually identical and there is an overlap in some measurements. Furthermore, they occur at the same altitudes—albeit in different habitats—in the Bolivian altiplano during the austral winter (Cabot & Serrano 1986, Cabot 1991). The two were for a long period differ- entiated on the basis of the relative distances between the tips of the third- and fifth-outermost primaries (Stresemann 1925), a feature subsequently disproved, leading to them being regarded as conspecifics (Farquhar 1998). Cabot & de Vries (2003) analysed the morphology and ecological behaviour of the two, proving their clear separability using other measurements and that they behave as species under the Biological Species Concept, although DNA studies have revealed their close similarity (Riesing et al. 2003), indicating that recent parapatric differentiation at high altitude in the Andes culminated with the retreat of the ice-packs at the close of the last glacial period, as suggested by Haffer (1967) and Dorst & Vuilleumier (1986) for birds of this region. These two species have the lowest known wing- loads of their genus (Cabot & de Vries 2003), an adaptation to the low atmospheric pressure in high-altitude ecosystems. The plumage of Buteo polyosoma (and B. poecilochrous) was studied by Vaurie (1962), who established that adults of B. polyosoma are of five different types. He also noted sexual dimorphism and that adult females have a red back, whilst males José Cabot & Tjitte de Vries 273 Bull. B.O.C. 2004 124(4) have a uniform grey back, although some possess a red patch as in females. The types defined by Vaurie (1962) are as follows. Type A: head, thighs and undertail- coverts dark brown or dark slate, with mantle and rest of underparts chestnut and unbarred. Type B: crown, nape and mantle the same colour as type A, but underparts white with narrow dusky-brown or grey bars that vary in intensity from broad and dense to unappreciable. Type C: body plumage including underwing- coverts grey (from pale slate to virtually black), with 50% having scattered reddish feathers on the mantle. Type D: upperparts grey and underparts and underwing white, with some showing some chestnut at the upper border of the mantle. Type E: crown and nape as in types A and B, but with variegated underparts: ventrally grey and brown, transversal pectoral band chestnut and rest of underparts and thighs having slate- and white-coloured bars. Pavez (1998) was first to describe the plumages of the pale phase of B. polyosoma and to relate different plumages to age. His study was based on plumage changes in captive Chilean birds from the first year and his results established that: (1) definitive adult plumage is reached more or less in the sixth year; (2) plumages are related to an age-dependent pattern of markings and coloration; (3) males between third and fifth years show some transitory characters, such as a reddish mantle, which correspond to definitive female plumage; and (4) definitive adult plumage is sexually dimorphic: males have a uniform grey back, females a brick- red patch. Here we describe, for the first time, sex- and age-related plumage changes in the dark morph, and also include a more specific description of colour patterns for the entire distribution of the pale morph, as described by Pavez (1998) for Chilean birds. Finally, the colour phases are established for the different ages (1-6 years). Material and methods We examined 160 specimens held at the Natural History Museum (Tring), Museum of Natural History (Stockholm), Zoological Museum (Copenhagen), Landes Museum (Linz), Museum d’Histoire Naturelle de Genéve (Geneva), Museo Regionale di Scienze Naturali (Turin), Institut Royal des Sciences Naturelles de Belgique (Brussels), Muséum National d’Histoire Naturelle (Paris), Estacion Biol6gica de Dofiana (Seville), Museo Nacional de Ciencias Naturales (Madrid), Museo Ecuatoriano de Ciencias Naturales (Quito), Museo de Ciencias Naturales “Mejia” (Quito), Museo de la Escuela Politécnica Nacional (Quito), and Museo Nacional de Ciencias del Instituto Técnico Superior “Bolivar” (Ambato, Ecuador). Specimens were available from Colombia (two), Ecuador (20), Peru (seven), Bolivia (24), Argentina (49), Chile (29) and the Falklands (21); four were of unknown origin. Four specimens of Buteo polyosoma exsul from the Juan Fernandez Islands were examined as comparative material. Some controversial and undated skins were identified and sexed on the basis of secondary length, wing length, wing depth and the shape of the wingtip, as per the José Cabot & Tjitte de Vries 274 Bull. B.O.C. 2004 124(4) range of values given by Goodall et al. (1951), de Vries (1973), Cabot (1991) and Cabot & de Vries (2003). The Stresemann criteria for distinguishing the species from B. poecilochrous were not used, as they are not diagnostic (Farquhar 1998, Cabot & de Vries 2003). Birds were classified according to similarities in plumage marks and coloration, enabling us to create a fixed number of categories that included all plumage types. Overall, these categories were relatively homogenous, despite the high degree of individual and geographical variation within plumages. In uniformly coloured areas of plumage, differences lie in ground-colour tones, as well as in their extent and distribution. Markings also vary in size, density and distribution. The age-related sequence of plumages was established from those birds that presented intermediate characteristics, denoting the change from one plumage category to another as feathers are replaced. The sequence of plumage changes was established by the simultaneous presence of old and new feathers, which were identified by wear on their distal edges or by differences in tone when the ground colour was similar. Changes in size, colour and distribution of markings were also taken into account, especially on the underparts. Moult patterns were not subject to close scrutiny. Captive birds in southern Iberia moulted in mid May and late September. Nevertheless, these periods may not correspond to moulting periods in their country of origin (Peru). Like Pavez (1998), we detected no protracted moult in the species. Neither were we able to discover how much individual variation—as occurs in large eagles—there is in the time birds take to acquire adult appearance. Specimens were photographed dorsally, ventrally and laterally and the images, once classified by age and sex, permitted comparative analysis between skins housed in different museums. Descriptions of the plumages of 12 live birds (three juveniles, two subadults and seven adults) in private zoos and raptor centres were made by means of twice-annual visits over three consecutive years to monitor changes. Live birds were sexed using molecular techniques (Ellegren 1996). The most distinctive plumage characteristics of the two morphs, including sexual differ- ences, are given in Table 1. Dark morph First-year: variable but sexes alike. Entirely dark chocolate-brown to uniform blackish brown, sometimes with cheeks paler and tinged tawny; crown and nape feathers have white bases visible on nape; mantle usually uniform; upperwing- coverts and scapulars have profuse and contrasting ochre or grey-ochre markings; secondaries dark-barred and distally pale-fringed; outermost primaries with blackish-brown tips, and ochre or creamy notches, especially on inner web; rump and uppertail-coverts dark chocolate-brown with concealed pale ochraceous or tawny spots; underparts with whitish to ochre-tawny spots, principally on mid and rear underparts, decreasing in size and merging into pale, scattered spotting on thighs and undertail-coverts; lesser and median underwing-coverts dark brown with José Cabot & Tijitte de Vries AGE First-year Second-year Third-year Fourth-year Fifth-year Sixth-year 2 Se Ny Bull. B.O.C. 2004 124(4) TABLE | Diagnostic characters according to age and sex in pale and dark phases of Buteo polyosoma. DARK PHASE Appearance wholly brown to blackish brown; upperparts marked ochre or grey- white; underparts sparsely pale or white spotted. Tail: above greyish brown with usually 14-18 close, narrow, irregular dark bands. As first-year but darker and more black- ish, less brown; more uniform; scattered marks on upperwing-coverts, tail has same pattern but slightly greyer than in previous plumage. Male: upperparts and head dark brown; mantle pale reddish tawny admixed brown; throat brown and rest of under- parts uniform brown suffused reddish; concealed pale marks on uppertail- coverts; tail washed white or greyish with bold narrow blackish undulating lines and broad subterminal black band, occasionally incomplete. Female: brick- red mantle, some feathers on upper man- tle have dark centres and dark shafts on lower mantle; underparts similar to male but brick red. Male: wholly bluish grey to dark slate- grey with faint brown wash and slight reddish dorsal coloration admixed grey; reddish pectoral band. Female: darker slate-grey with rich, pure and intense brick red dorsal patch; below also brick red except throat, thighs and undertail- coverts. Male: entirely grey with scattered red- dish-and-grey feathers on back and cen- tral chest. Female: darker, with grey bib from chin to mid breast; rest of plumage similar to fourth-year birds. Male: all grey with sometimes just a few vestigial red feathers on the mantle and, very occasionally, the breast. Female: essentially as previous year. PALE PHASE Malar stripe and upperparts dark brown with tawny-ochre markings; supercilium, cheeks and underparts pale ochraceous with dark streaks on throat and breast-sides; rest of underparts and thighs have brownish diamond-shaped marks which progressively decrease in size, merge and become more widely spaced towards tail; tail more brownish than in first-year dark phase. As first-year but mid and rear underparts reticu- lated or boldly marked with rufescent-brown to rusty-orange bars, which decrease in size, becoming more widely spaced and diffuse towards undertail-coverts and thighs. Male: top and sides of head blackish brown, dor- sal patch reddish tawny admixed brown; below whitish with underparts unmarked or with scant streaks on breast-sides; rest of underparts and thighs barred rusty-brown, stronger towards flanks, with finer and more widely spaced bar- ring nearer tail. Tail as dark phase of same age but lacks greyish wash and has finer transverse black lines. Female: darker, with obvious brick red dorsal patch extending towards nape and from neck-sides towards flanks; underparts more barred. Male: upperparts grey, with slight brownish tinge; top of head also grey and lower half white; brick red mantle; below white, finely barred dark chestnut to grey from mid breast to vent and thighs. Female: underparts as male, although somewhat more barred and has reddish-chestnut flanks and spots either side of breast. Male: similar to fourth-year birds, with small or poorly defined dorsal patch consisting of just a few reddish feathers; central vent and thighs with fine grey bars or vermiculations. Female: black- ish-grey barring finer than in fourth-year; grey spots on breast-sides, and greyish flanks. Male: as fifth-year but white below with grey vermiculations on thighs and flanks. Female: essentially as fifth-year. José Cabot & Tjitte de Vries 276 Bull. B.O.C. 2004 124(4) pale dots; uppertail greyish or blackish grey, with closely spaced irregular brownish bars or extensive mottling. Second-year: sexes alike. Like first-year but darker, from brownish to extremely dark sooty black. Incipient dimorphism usually detectable: males normally uniformly darker than females; markings restricted to median and greater upperwing- and uppertail-coverts; underparts in both sexes have scant pale spotting largely restricted to flanks; underwing almost lacks markings. Some show a pale wash on cheeks; tail greyer and with same pattern of dark barring as in previous plumage. Third-year: sexes differ. Male: crown, head-sides, nape and hindneck blackish brown; crown and nape feathers have visible white bases; mantle reddish or reddish brown with some two-toned feathers having dark brown centres and reddish fringes forming a more or less consistent and homogeneous patch; rest of upperparts brownish black with concealed cinnamon-tawny scapular marks, and secondaries and primaries have dark barring on outer webs; outermost primaries have black tips, but inner primaries and secondaries may be fringed white distally; uppertail-coverts blackish with concealed pale spots; underparts reddish brown except throat, thighs, vent and undertail-coverts, which are uniform blackish brown; underwing-coverts also blackish with a few small dots; tail whitish, washed grey, especially on sides, with bold transversal black lines and a more or less complete broad subterminal black band; below a fine pale grey band and feathers finely fringed white distally. Female: usually like male but darker and reddish areas brighter; mantle uniform and brighter brick red, this colour sometimes extending from crown to scapulars and dorsal patch, and may also include neck-sides. Remarks: specimens in moult from second- to third-year show great individual variation in number of old brown feathers mixed with new reddish ones on dorsal patch and underparts. Aside of flight-feathers and tail, some females at this age and the next year can be extensively erythristic. Fourth-year: sexes differ. Male: head and upperparts mid grey to uniform dark slate-grey, frequently with almost imperceptible brownish tones; nape feathers have visible white bases and black tips, forming conspicuous black-and-white nuchal spot; dorsal reddish patch consists of two-toned feathers, with grey centres and chestnut fringes, on hindneck and upper mantle; lesser and median upperwing- coverts uniform grey; greater coverts, secondaries and primaries grey with irregular close dark barring. Primaries and secondaries pale-tipped with blackish subtermi- nal coloration visible in flight on upper and lower surfaces as a broad blackish distal band that follows outline of wing and remains evident in subsequent plumages; underparts uniform grey with a transversal reddish pectoral band; lesser and median underwing-coverts uniform pale grey, sparsely spotted; greater underwing-coverts pale greyish with black barring; tail as previous plumage but whiter and has a José Cabot & Tjitte de Vries 274 Bull. B.O.C. 2004 124(4) blacker, complete subterminal band. Female: upperparts dark slate-grey to slate- grey, similar to previous plumage, but has dorsal patch more intense and purer; underparts extensively reddish except throat, neck, thighs and belly, which are uniform slate-grey. Undertail-coverts, wing and tail as male and remain as such in subsequent plumages. Fifth-year: sexes differ. Male: as previous plumage but greyer, lacking brownish tones, ground colour varying from lead or blue-grey to uniform blackish slate; the few grey-and-red feathers in upper mantle not forming a defined patch; rump blackish and upper- and undertail-coverts have white distal fringes; underparts uniform grey with scattered reddish feathers that may or may not form a defined transversal upper breast-band; lesser and median underwing-coverts with scant pale grey spotting and same barring as on greater underwing-coverts. Female: upperparts similar to fourth-year plumage but with a shorter, reddish dorsal patch from base of hindneck to mantle or mid scapulars; underparts have a uniform grey bib, paler on throat; below, a broad uniform red band restricted to mid breast; flanks with mixed grey and reddish tones; belly, thighs and undertail-coverts same blackish-grey colour. Older than five years: sexes differ. Male: appears all uniform grey, sometimes with a few grey-and-red feathers on mantle and, more rarely, in mid chest, which are lost in subsequent years, although some persist in oldest live birds. Female: grey areas darker than in male in all plumages. Red-and-grey pattern similar to fifth-year with no obvious changes. Remarks: Exceptionally, an adult female from Colchagua (Cordillera, Chile, BMNH 1844.44.10.7.1) did not have thighs and lower chest uniform grey, as is usual in B. polyosoma, but instead showed faint, fine and well-spaced whitish bars over steel grey on belly and thighs, typical of defini- tive plumage of dark-morph B. poecilochrous (Gurney 1879, Cabot & de Vries unpubl.). This unusual bird has subsequently been reidentified (twice as B. polyosoma and once as B. poecilochrous) and was discussed by experienced taxonomists such as Hellmayr (1932) and Vaurie (1962). Farquhar (1998) also found, amongst the specimens he examined, a male dark-morph B. polyosoma with barred rear underparts. Pale morph First-year: sexes alike. Upperparts dark brown; feathers on crown, nape and hindneck pale-bordered, affording streaked appearance, with white feather bases to crown and nape (visible on latter); mantle usually more uniform or feathers have pale fringes; upperwing-covert and scapular feathers have pale fringes coarsely marked with ochraceous yellowish to tawny cinnamon; rump brown with ochre or tawny spots; uppertail-coverts white with cinnamon-coloured marks; secondaries and primaries browner than dark morph; supercilium and cheeks pale cream to José Cabot & Tjitte de Vries 278 Bull. B.O.C. 2004 124(4) rusty, frequently with short, fine dark streaks; malar stripe dark brown; underparts creamy to ochraceous; some fine dark streaks on chin; feathers on neck-sides and upper breast have some dark shaft-streaks and a tear-shaped base, central parts more uniform; mid and rear underparts clearly delimited by dense V-shaped rusty to rufous or mahogany marks, browner on sides of mid underparts, which radiate, decrease in size and become less pointed on rear underparts and thighs; a few small dark marks on undertail-coverts; underwing-coverts beige with dark markings. Uppertail grey-brown, paler, but with same barred pattern as first-year dark morph. Second-year: sexes alike, as preceding plumage. Upperparts similar, with profuse pale marks and feathers on dorsum broadly fringed pale ochre to cinnamon, especially on mantle-sides, where markings apparently more rufous or cinnamon in females; in some, median and lesser upperwing-coverts and scapulars are extensively marked tawny cinnamon or admixed brown; rump brown with ochre or tawny spots and uppertail-coverts cinnamon; throat faintly whitish, but underparts similarly or less marked; mid and rear underparts reticulated or have coarse rusty to ferruginous bars; markings diminish towards tail and merge into barring on thighs and vent; slight barring on undertail-coverts. Uppertail more greyish, but sometimes washed cinnamon and has same markings, the ultimate dark bar distally more obvious and slightly broader. Third-year: sexes differ. Male: head, nape and sides dark brown or blackish, crown and nape feathers with white bases (visible on latter), and rest of upperparts brown-grey, with a pale chestnut patch on mantle sometimes extending onto scapulars; occasionally reddish feathers with dark centres, usually on upper mantle, with dark lines along shafts on lower mantle; upperwing-coverts and scapulars have markings as in rest of previous plumage; rump brown with ochre marks and uppertail-coverts cinnamon; underparts whitish with unmarked, uniform bib, or some dark lines on sides; mid and rear underparts have rusty-orange to brown- mahogany barring, tending to ferruginous, which decreases in size and in intensity near tail; thighs similarly barred. Tail white with broad black subterminal band bordered below by a narrow greyish band; distally bordered white with fine, well- spaced black transversal lines above, varying in number. Underwing-coverts whitish with some dark markings. Female: crown blackish brown with darker back; mantle with intense brick-red patch, which in some reaches from nape to scapulars; also extends to neck-sides, forming reddish patch either side of bib, extending to flanks and underwings, which appear reddish or cinnamon-tinged, admixed grey; rest of underparts similar to male, although more ferruginous and more heavily marked. Fourth-year: sexes differ. Male: similar to preceding plumage; upperparts grey, from silvery to bluish lead grey without brownish tone; visible white bases to feathers on nape; dorsal patch more intense brick red. In some, patch restricted to José Cabot & Tjitte de Vries 279 Bull. B.O.C. 2004 124(4) shoes WIT ° year 3° year ° year 5° year ° year Figure 1. Dark-phase plumage patterns in B. polyosoma according to age and sex. Numbers correspond to calendar year. Figure. 2. B. polyosoma pale-phase male plumage patterns according to age. Numbers correspond to calendar year. (1) = late. José Cabot & Tjitte de Vries 280 Bull. B.O.C. 2004 124(4) mantle, but in others extends to scapulars. Patch also varies from almost uniformly reddish to grey due to number of red-and-grey feathers; upperwing as dark morph, although paler; rump dark grey or brownish grey, and uppertail-coverts whitish with grey barring; underparts generally white, with grey or blackish-grey barring and becoming finer and less perceptible ventrally; undertail-coverts almost uniform white with few dark markings; lesser and median underwing-coverts whitish, almost lacking markings, and greater coverts pale grey with dark barring; tail as preceding plumage, although whiter with subterminal band blacker and transversal lines finer and better defined. Female: upperparts darker with a black crown in some; dorsal patch uniform; more extensive, intense brick-red mantle, with dark streaks on upper mantle, extending to form reddish-grey spots either side of chest; in some red dorsal patch can extend from scapulars to mid crown; rump darker slate-grey and uppertail-coverts whitish with grey to black barring. Underparts like male but with blacker and slightly broader barring; sides have black to grey barring with chestnut- or rusty-toned markings. Fifth-year: sexes differ. Male: essentially similar to previous plumages but upperparts paler grey with visible dark shafts; feathers on nape have white bases and black tips forming a visible patch; small red patch restricted to upper mantle or a few irregularly distributed red-and-grey feathers; underparts with grey markings either side of bib; mid and rear underparts and thighs with transverse dark lines or, sometimes, almost imperceptible vermiculations, becoming more obvious on lower breast-sides; flanks have transverse lines and grey markings; lesser and median underwing-coverts purer white, greater underwing-coverts white to greyish with blackish barring. Female: dorsal plumage similar to previous year; less barred on underparts; flanks with grey markings and barring as male. Older than five years: sexes differ. Male: upperparts totally grey or with scattered red-and-grey feathers on mantle; underparts tend to be more uniform with age and gradually lose transverse lines on chest and thighs, although faint vermiculations almost always detectable. Female: little change, except a gradual loss in intensity and width of transverse lines on underparts, which are always more obvious in males. Remarks: in both dark and pale morphs, some have a white or ochraceous forehead, or a spot either side of bill base. To a greater or lesser degree, some have secondaries and tips of innermost primaries with a white or whitish fringe. Some juveniles of both morphs have uniformly blackish tips to outermost primaries, whilst others exhibit some pale spotting on inner webs or spots on inner and outer webs that form contrasting pale brown barring. The sequences of age-related plumage changes, from juvenile to definitive adult, in both sexes are summarised in Fig. 1. José Cabot & Tjitte de Vries 281 Bull. B.O.C. 2004 124(4) Relationship between the morphs Pale birds predominated (86.1%; n=129) over dark in our sample; only four dark- phase birds (two from Tucuman, Argentina, one from Colchagua, Chile, two from La Paz, Bolivia) are known away from southernmost South America (in European collections none was found from Colombia, Ecuador or Peru); all other dark specimens (82.4%; n=25) are from southern Argentina and Chile. This approxi- mates to the percentages found by de Vries (1973) (82.7 %, n=75) and by Vaurie (1962) (90%, n=242) for pale birds. Field observations reveal a much greater proportion of pale birds. Bellati (pers. comm.) recorded only six dark birds (1.2%) of a total of 490 observed in non- Andean Patagonia (Bellati 2000). Dondazar et al. (1993) found only pale birds in Patagonia, as did JC in Andean Bolivia during a five-year study. Furthermore, all 13 live birds studied from Peru were pale morphs, as were six observed in March 2003 in Andean Ecuador. Discussion Morphs, delayed plumage maturation and plumage change All plumage types of all birds examined can be classed as belonging to either pale or dark morphs. Such coloration is not uncommon in Buteo (Brown & Amadon 1968) and has been recognised in B. polyosoma (Reynolds 1935, Housse 1945, Woods 1988). The rufous morph suggested by Goodall et al. (1951) and Johnson (1965) on the basis of dark-morph specimens with extensively chestnut body plumage does not exist. Pale-phase birds—also referred to as ‘normal-phase’ birds (Jiménez 1995)—are more abundant, both in the wild and in museums. Dark birds are rare over much of the species’ distribution. The relatively numerousness of dark-morph birds in collections is explained by the large number of specimens in the Natural History Museum (Tring), in which the Falklands and the southern tip of South America— where dark birds are commoner (Reynolds 1935, Woods 1988)—are particularly well represented. Other European museums have a majority of birds from Argentina and Chile, i.e. the region where a large percentage of southern birds winter. Another factor is the possible bias shown by collectors towards rarer dark birds, as a means of equalling numbers in a series of both colour morphs. Age- and sex-related plumage changes in pale birds were briefly mentioned by Reynolds (1935) and subsequently described by Housse (1945) and Goodall et al. (1951), who calculated 3-5 years as the time needed to reach definitive plumages. Our results and those of Pavez (1998) have established a period of six years. This is long considering the size and weight (c.1 kg: Cabot 1991, Jiménez 1995) of the species. José Cabot & Tjitte de Vries 282 Bull. B.O.C. 2004 124(4) Delayed maturation only occurs in the phylogenetically closest species that constitute the oldest cluster within Buteo (Riesing et al. 2003). Along with B. polyosoma, these species are: B. poecilochrous (Cabot & de Vries unpubl.), B. albicaudatus (Lehmann 1945, Torres Barreto 1986) and B. melanoleucus. Papers on plumage change in B. polyosoma published in Spanish have been all but ignored, unlike publications in English by European and North American authors based on analyses of incomplete series’ of skins that do not provide evidence for the existence of sequential plumage variation. Thus, Vaurie (1962), Brown & Amadon (1968) and Farquhar (1998) discussed plumage, age and sexual dimorphism in B. polyosoma without being aware of its sequential pattern of plumage change. This process of plumage change concludes with a sexually dimorphic terminal plumage, somewhat unusual in Buteo. Prior to this, subadult males pass through a stage in which they acquire coloration and patterns resembling the final female plumage of their respective phases. Acquisition of adult female markings by subadult males also occurs in B. poecilochrous, a polyandrous species in which up to four males may cooperate in chick-raising (Solis & Black 1985, Coello 1997). However, no cases of polyandry have been recorded for B. polyosoma anywhere in its vast range (Jiménez 1995). The following features stand out in this process of delayed maturation. Both morphs coincide in the following: retention of juvenile characteristics during the first two years of life, with incipient sexual dimorphism occurring in the second year onwards; and immature males (third and fourth years) imitate definitive adult female plumage of their respective morphs. Conversely, female erythrism reaches its peak at this age, as if female plumage always tends to differ from that of males. Fifth-year or older birds show marked sexual dimorphism (unusual in this genus): thus, males lose their female characteristics whilst females retain plumage patterns similar to subadults. Fifth-year Chilean males show similar reddish dorsal coloration to females (Pavez 1998). We have observed southern males—presumably of this age group— with uniform white underparts and extensive reddish dorsal areas. Nevertheless, throughout the rest of the species’ range birds of this age tend to have less reddish dorsal coloration and in live, fourth-year Peruvian males the reddish dorsal area is relatively small. This seems to indicate that the process of delayed maturation varies between geographically distinct populations. Such variations can be linked to obvious differences in size, given the direct relationship between longevity and body size. The largest birds occur in the southernmost part of the species’ range, and the smallest in coastal Peru and Ecuador (de Vries 1973, Fjeldsa & Krabbe 1990, Cabot & de Vries 2003). The two morphs differ in regard to sexual dimorphism in body plumage. Pale- phase birds of both sexes have virtually identical underparts but different dorsal plumages, whilst dark-phase birds maintain differences in upperparts and underparts. José Cabot & Tjitte de Vries 283 Bull. B.O.C. 2004 124(4) Vaurie (1962) and de Vries (1973) assumed that birds with white tails (and a black subterminal band) were sexually adult, although, as we have seen, this characteristic is reached as early as the third year. Reynolds (1935), who claimed to have climbed to hundreds of nests, mentioned that it is not unusual to find breeding pairs in which one bird still has the brownish coloration mixed with white or red of the following plumage stage. This indicates that sexual maturation is not delayed until the sixth year. Mate selection remains mysterious, and we should note that it is surprising that white-tailed males (3-5 years old) should moult through an incomplete, dullish reddish-brown female plumage, and that in these same age- classes females should become very prominent in their brilliant reddish-brown colours. Vaurie’s phases Vaurie (1962) established five adult plumage types, four of which coincide with those described here. Types B and D of Vaurie’s classification correspond to defini- tive adult male and female pale-morph plumages respectively (Pavez 1998), whilst types C and A coincide with definitive dark-morph male and female plumages (over five years old). Vaurie (1962) was correct in establishing these categories in his heterogeneous sample, despite the existence of delayed maturation with several successive age-classes appearing before a definite plumage phase had been recognised. Likewise, no accurate criteria existed then for separating B. polyosoma from B. poecilochrous in the hand. This we see in Vaurie’s type E (birds with reddish backs and breasts, and reddish and grey-barred with white rear underparts and thighs). Vaurie’s type E does not correspond to any plumage phase in B. polyosoma, rather it represents a dark-phase B. poecilochrous female prior to the acquisition of definitive plumage. In its final adult plumage B. poecilochrous loses the transverse chestnut pectoral band and retains the white-grey or whitish black, strongly barred, mid and rear underparts and tibial feathers (Gurney 1879, Lehmann 1945, Johnson 1965). Such confusion between B. polyosoma (uniform underparts) and B. poecilochrous (strongly barred) is also obvious in Fig. 196, Plate 62 of Ferguson-Lees & Christie (2001). The final characteristic plumage of a dark-phase adult female is shown in Fig. 184, Plate 18 (Thiollay 1994), although the uniform grey bib and rear underparts are less extensive than in real life. Brown-headed specimens in Vaurie’s type A represent subadult dark-phase females, 34 years old, which will eventually moult to a grey head and bib, uniform grey and unbarred rear underparts, with a transverse chestnut pectoral band, but this is not definitive plumage. Acknowledgements We are most grateful to the following: Dr Jon Fjeldsa for his very useful suggestions and corrections, and the following museum curators who kindly permitted access to specimens and also sent material: Dr Josefina Barreiro, Curator of Birds, Museo Nacional de Ciencias Naturales (Madrid), Dr Sonia Sandoval, Executive Director, Museo de Ciencias Naturales (Quito), Dr Marta Espinosa, Director, Museo de Ciencias Naturales “Mejia” (Quito), Dr Cristina Leén, Director, Museo del Instituto Técnico José Cabot & Tjitte de Vries 284 Bull. B.O.C. 2004 124(4) Superior “Bolivar” (Ambato), Dr Gerhard Aubrecht, Landes Museum (Linz), Dr Alice Cibois and Dr Manuel Ruedi, Museum d’Histoire Naturelle de Genéve (Geneva), Dr Geraldine Veron, Muséum National d’ Histoire Naturelle (Paris), H. Baagoe, Zoological Museum, University of Copenhagen, Dr Goran Frisk, Museum of Natural History (Stockholm), Dr René W. R. J. Dekker, Naturalis (Leiden), Dr Kees Roselaar, Zoological Museum (Amsterdam), Dr Lenglet, Institut Royal des Sciences Naturelles de Belgique (Brussels), and Dr Claudio Pulcher, Museo Regionale di Scienze Naturali (Turin). We also thank staff of the Natural History Museum (Tring) for their kind attention, Dr Nigel Collar for his assistance and Les & Marjorie Newman of Berkhamsted for their hospitality to JC. We are also most indebted to Maria Angeles Prieto, Fernando Feds Costilla, José Luis Ortiz and Juan Ignacio Caballo, who allowed us to obtain data from live birds, and to Esther Aukje, Martje Irene, Therese Isabel de Vries and Mike Lockwood who corrected the English text. References: Bellati, J. 2000. Comportamiento y abundancia relativa de rapaces de la Patagonia extraandina Argentina. Orn. Neotrop. 11: 207-222. Brown, L. & Amadon, D. 1968. Eagles, hawks and falcons of the world. McGraw-Hill, New York. Cabot, J. 1991. Distribution and habitat selection of Buteo polyosoma and B. poecilochrous in Bolivia and neighbouring countries. Bull. Brit. Orn. Cl. 114: 199-209. Cabot, J. & Serrano, P. 1986. Data on the distribution of some species of raptors in Bolivia. Bull. Brit. Orn. Cl. 106: 170-173. Cabot, J. & de Vries, T. 2003. Buteo polyosoma and Buteo poecilochrous are two distinct species. Bull. Brit. Orn. Cl. 123: 190—207. Coello, M. 1997. Biologia reproductiva y habitos alimenticios de Buteo poecilochrous en el paramo de la Reserva Ecoldégica Antisana, Ecuador. Thesis. Pontificia Univ. Catélica del Ecuador, Quito. Chapman, F. M. 1926. The distribution of bird-life in Ecuador. Bull. Amer. Mus. Nat. Hist. 55. de Vries, T. 1973. The Galapagos Hawk. An eco-geographical study with specific reference to its sys- tematic position. Ph.D. thesis. Free Univ. of Amsterdam. Donazar, J. A., Ceballos, A., Travaini, A. & Hiraldo, F. 1993. Roadside raptor surveys in the Argentinean Patagonia. J. Raptor Res. 27: 106-110. Dorst, J. & Vuilleumier, F. 1986. Convergences in bird communities at high altitudes in the tropics (espe- cially the Andes and Africa) and at temperate latitudes (Tibet). Pp. 120-149 in: High-altitude sub- tropical biogeography. Oxford Univ. Press, New York. Ellegren, H. 1996. First gene on the avian W chromosome (CHD) provides a tag for universal sexing of non-ratite birds. Proc. Roy. Soc. Lond. B 263: 1635-1641. Farquhar, C. C. 1998. Buteo polyosoma and B. poecilochrous, the “Red-backed Buzzards” of South America are conspecific. Condor 100: 27-43. Fjeldsa, J. & Krabbe, N. 1990. Birds of the high Andes. Zool. Mus., Univ. of Copenhagen & Apollo Books, Svendborg. Ferguson-Lees, J. & Christie, D. A. 2001. Raptors of the world. Christopher Helm, London. Goodall, J. D., Johnson, A. W. & Philippi, R. A. 1951. Las aves de Chile, su conocimiento y sus costumbres. Platt Establecimientos Graficos, Buenos Aires. Gurney, J. H. 1879. Note upon three American raptorial birds apparently new to science. [bis 3: 171-178. Haffer, J. 1967. On the dispersal of highland birds in tropical south and central America. El Hornero 10: 437-438. Hellmayr, C. E. 1932. The birds of Chile. Field Mus. Nat. Hist., Zool. Ser. 19. Housse, R. 1945. Las aves de Chile, en su clasificacién moderna. Ed. Universidad de Chile, Santiago. Jaksi, F. M, Silva S., Marquez P. & Contreras, L. C. 1991. Food habits of Gurney Buzzard in pre-Andean ranges and the high Andean Plateau of northernmost Chile. J. Raptor Res. 25: 116-119. Johnson, A. W. 1965. The birds of Chile and adjacent regions of Argentina, Bolivia and Peru. Platt Establecimientos Graficos, Buenos Aires. Jiménez, J. E. 1995. Historia natural del Aguilucho Buteo polyosoma: una revision. Hornero 14: 1-9. José Cabot & Tjitte de Vries 285 Bull. B.O.C. 2004 124(4) Jiménez, J. E. & Jaksi, F. M. 1991. Behavioral ecology of Red-backed Hawks in central Chile. Wilson Bull. 103: 132-137. Lehmann, F. C. 1945. Rapaces colombianas: subfamilia Buteoninae. Rev. Univ. Cauca (6): 81-114. Pavez, E. F. 1998. Observaciones sobre el patron de coloraciédn en machos y hembras de Aguilucho (Buteo polyosoma, Quoy y Gaimard, 1924). Bol. Chil. Orn. 5: 21-23 de la Pema, M. R. 1995. Guia de aves argentinas, vol. 2. LOLA, Buenos Aires. Philippi, R. A. 1942. La verdadera situaci6n sistematica de los Accipitridae descritos por R. A. Philippi. Hornero 8: 179-189. Quoy, J. R. C. & Gaimard, J. P. 1824. Buse Polyosome. P.92 in Freycinet, M. L. (ed.) Voyage autour du monde, vol. 3. Paris. Reynolds, P. W. 1935. Notes on the birds of Cape Horn. /bis (13) 5: 65-101. Riesing, M. J., Kruckenhauser, L., Gamauf, A. & Haring, E. 2003. Molecular phylogeny of the genus Buteo (Aves: Accipitridae) based on mitochondrial marker sequences. Mol. Phyl. & Evol. 27: 328-342. Solis, C. & Black, J. 1985. Anidaci6n de Buteo poecilochrous en Antisana. Rev. Geogr, Quito 21: 132-142. Stresemann, E. 1925. Raubvogelstudien, X. Die weissschwanzingen Bussarde Siid-Amerikas. J. Orn. 73: 309-319. Swann, H. K. 1922. A synopsis of the Accipiters (diurnal birds of prey). Revised edn. London. Thiollay, J.-M. 1994. Family Accipitridae (hawks and eagles). Pp. 52-206 in del Hoyo, J., Elliott, A. & Sargatal, J. (eds.) Handbook of the birds of the world, vol. 2. Lynx Edicions, Barcelona. Torres Barreto, A. 1986. Cetraria Neotropical colombiana, manual de volateria experimental con rapaces suramericanas. Itto. Colombiano de Cultura Hispanica. Bogota. Vaurie, C. 1962. A systematic study of the Red-backed Hawks of South America. Condor 64: 277-290. Woods, R. W. 1988. Guide to birds of the Falkland Islands. Anthony Nelson, Oswestry. Addresses: J. Cabot, Estacién Biolégica de Dofana, Av. Maria Luisa s/n. 41013, Seville, Spain, e-mail: cabot@ebd.csic.es. T. de Vries, Dpto. Biologia, Pontificia Universidad Catélica del Ecuador, Apartado 17-01-2184, Quito, Ecuador, e-mail: tdevries@puce.edu.ec © British Ornithologists’ Club 2004 Recent observations of Dull-coloured Grassquit Tiarts obscura in Mato Grosso reinforce its status as an austral migrant to south-west Brazil by Andrew Whittaker & Braulio Carlos Received 25 September 2003 On 16 September 2000, at Coxip6 de Ouro, Cuiaba, Mato Grosso, whilst leading a bird tour, AW heard an unknown call in response to his imitation of Ferruginous Pygmy-owl Glaucidium brasilianum. Tracking this call to some low, dry thorny scrub bordering taller gallery forest, he located two unfamiliar dull-coloured Fringillidae. AW recommenced the ow! imitations and the birds approached even closer, permitting excellent views at 5—6 m through 10 x 42 binoculars in perfect light. The following field marks were noted: two small c.10.5—11.0 cm nondescript Andrew Whittaker & Braulio Carlos 286 Bull. B.O.C. 2004 124(4) dull seedeaters, olive-brown above with a slightly paler buffy eye-ring and one had slightly richer brownish fringes to the greater wing-coverts. The only distinctive feature shown by both birds was the short, stubby bicoloured bill, with pale yellow- ish lower mandible contrasting with a darker dusky upper mandible. Underparts were a dirty off-white sandy coloration, paler than the browner upperparts. The general nondescript plumage combined with the distinctive bicoloured bill confirmed that they were Tiaris obscura. AW recognised the significance of this record, but as the birds were silent and he lacked photographic equipment, documentation was impossible. The two Tiaris obscura loosely associated with two Red Pileated-finches Coryphospingus cucullatus, which had also approached closely in response to the owl imitation. AW shared this exciting record with BC, alerting him to the possible presence of the species in the northern Pantanal during the austral winter. On 8 March 2002, near Poconé, Mato Grosso, in open grassland along the Transpantaneira highway leading into the northern Pantanal (16°19’S, 56°38’W), BC heard an unknown vocalisation that reminded him of the cut of TZ. obscura on Mayer (2000). In response to playback of this recording, a single 7: obscura immediately approached to within 2 m, remaining very agitated, but silent. Thus, again, audio recordings could not be obtained to authenticate the record. BC noted the bicoloured bill as extremely evident, yellowish below with a dark dusky maxilla, and that the bird had an indistinct buff eye-ring. Following playback of G brasilianum the only other seedeater to approach was an immature male Dark-throated Seedeater Sporophila ruficollis. Again, on 16 October 2002, at Chapada dos Guimaraes, Mato Grosso, BC observed 2-3 T. obscura at the transition between gallery forest and shorter dry scrub. All were easily distinguished by their distinct bicoloured bills. They remained silent and were in a monotypic flock, without any other seedeaters. Bates (1997) drew attention to two overlooked historic T. obscura specimens housed in the American Natural History Museum (AMNH), collected by H. H. Smith at Chapada, Mato Grosso, Brazil, on 29 July and 30 August 1885. These two (AMNH 32582 and 32588) had been overlooked for over a century, having been misidentified as female Sooty Grassquits Tiaris fuliginosa (e.g. Allen 1891, Naumburg 1930, Hellmayr 1938). They are the first Brazilian specimens of 7: obscura. Bates (1997) suggested they are T: o. obscura, which breeds in Paraguay and Argentina, and is a regular visitor during the austral winter to the eastern lowlands of Bolivia, Paraguay and northern Argentina. Bates (1997) went on to state that these records represent non-breeding extralimitals and that additional information is required to determine the status of the species in the region. Our recent field observations reinforce the impression that 7: o. obscura is an austral migrant to south-west Brazil, which due to its cryptic similarity in the field to several species of female seedeaters Sporophila sp. and female grassquits Tiaris sp. has most probably been long overlooked. We hope our report will alert observers to pay critical attention to female-type Sporophila and Tiaris, particularly during the austral winter, and permit them to key into T. obscura. We recommend Andrew Whittaker & Braulio Carlos 287 Bull. B.O.C. 2004 124(4) detailed field searches for 7: obscura in south-west Brazil during the austral winter to clarify its range and status in Brazil. References: Allen, J. A. 1891. A collection of birds from Chapada, Mato Grosso, Brazil, made by Mr. Herbert H. Smith. Bull. Amer. Mus. Nat. Hist. 3: 337-380. Bates, J. M. 1997. Distribution and geographic variation in three South American grassquits (Emberizinae, Jiaris). Pp. 91-110 in Remsen, J. V. (ed.) Studies in Neotropical ornithology honor- ing Ted Parker. Orn. Monogr. 48. Hellmayr, C. E. 1938. Catalog of birds of the Americas and adjacent islands. Field Mus. Nat. Hist, Zool. mers, pt. LI). Mayer, S. 2000. Birds of Bolivia 2.0. CD-ROM. Bird Songs International, Westernieland. Naumburg, E. M. B. 1930. The birds of Mato Grosso, Brazil: a report of the birds secured by Roosevelt- Rondon Expedition. Bull. Amer. Mus. Nat. Hist. 60: 1-432. Addresses: Andrew Whittaker, Conjunto Acariquara, Rua Samaumas 214, Manaus 69085-053, Amazonas, Brazil, e-mail: Andrew @birdingbraziltours.com. Braulio Carlos, Rua Barao de Melgaco 130, apt. 2631, Cuiaba 78025-300, Mato Grosso, Brazil. © British Ornithologists’ Club 2004 A specimen of Cape Petrel Daption capense from north-east Brazil by Caio Fosé Carlos, feremiah Trimble & Carmem Elisa Fedrizzi Received 8 October 2003 Cape Petrel Daption capense is a mid-sized procellariiform which breeds on subantarctic islands throughout the Southern Ocean, and the Antarctic Peninsula and continent (Harrison 1983, del Hoyo et al. 1992). On dispersal, which commences February—March, it regularly occurs north to c.25°S, and has reached Ecuador and Colombia, and even Mexico and northern California; in the Atlantic, it reaches Uruguay and Brazil, north to Rio de Janeiro (Harrison 1983, Sick 1997). As part of ongoing research on seabirds off north-east Brazil, we located an old, and apparently overlooked, specimen of the species at the Museum of Comparative Zoology (MCZ), Harvard University, Cambridge, Massachusetts. The bird (MCZ 226730, adult, sex unknown) was collected by George H. Mackay at Cabo de Sao Roque (05°29’S, 35°16’W), on the coast of Rio Grande do Norte, near the mouth of the Maxaranguape River (Paynter & Traylor 1991), on 9 June 1863. This record extends the species’ range north more than 2,000 km in the western Atlantic (Blake 1977, Pinto 1978, Harrison 1983, Sick 1997, Vooren & Brusque 1999). Measurements (mm) of the skin are: culmen 33; wing 262; tail 99 and tarsus 44. Plumage: upperparts with black mantle merging into white back and rump, both Carlos et al. 288 Bull. B.O.C. 2004 124(4) broadly marked with black chevrons recalling a checkerboard; wings mostly black; and tail mostly black with white base. Given the plumage and morphometrics, the specimen is of nominate D. c. capense, which breeds on subantarctic islands in the western hemisphere (e.g. South Georgia and the South Shetlands), the Antarctic Peninsula and continent (Harrison 1983, del Hoyo et al. 1992). The other subspecies, D. c. australe breeds at the Snares, Antipodes, Bounty and Campbell islands, off New Zealand, and is smaller and has more white on the upperparts (Harrison 1983). For a comparison of the plumages of these taxa see Fig. 1. How could a southern polar procellariiform reach the warm waters of north-east Brazil? During the austral winter, many birds from the Southern Ocean undertake regular northward movements along the Brazilian coast to c.22°S, mainly occurring at rich upwelling areas like those of the Cabo Frio region, Rio de Janeiro, or high- productivity areas in south and central Sao Paulo (Olmos et al. 1995, Sick 1997). More rarely, some reach waters off north-east and north Brazil. For instance, White- chinned Petrel Procellaria aequinoctialis and Atlantic Petrel Pterodroma incerta have been recorded at the mouth of the Amazon (Novaes 1959, Teixeira et al. 1996), Light-mantled Sooty Albatross Phoebetria palpebrata in coastal Bahia (Sampaio & Castro 1998), and Snowy Sheathbill Chionis albus in Pernambuco (Telino Junior et al. 2001). Strong winds associated with cold fronts originating in Sao Roque, Bi Figure 1. Cape Petrel Daption capense capense specimen from Cabo de S40 Roque (MCZ 226730), Rio Grande do Norte, Brazil, and a specimen of D. c. australe from the Snares Islands, New Zealand (MCZ 300895) (Jeremiah Trimble) Carlos et al. 289 Bull. B.O.C. 2004 124(4) Antarctica may be important in explaining the apparently anomalous occurrence of such birds north to the equator. The appearance of Southern Ocean birds in north-east Brazil, a region dominated by sandy beach coasts where the sea is generally nutrient-poor, may be linked to the high outflow of nutrients from such mainland ecosystems as large estuaries and associated mangrove swamps, e.g. in the Canal de Santa Cruz estuar- ine complex, Pernambuco, and the mouth of the Sao Francisco River, Alagoas (Azevedo Junior 1998, Souza 1993). Thus, the region of Cabo de S40 Roque, which is only c.3 km north of the mouth of the Maxaranguape River, may constitute a relatively productive area, permitting the occurrence of subantarctic birds such as Cape Petrel and Southern Fulmar Fulmarus glacialoides, the latter confirmed by three skins at MCZ (186306, 186307, 226729, all taken, on 9 June 1863, at Cabo de Sao Roque, and collected by George H. Mackay). Finally, it must be stressed that there are few studies on the distribution of seabirds off north-east Brazil. Antas (1991) noted that ornithologists interested in seabirds are mainly resident in southern Brazil. Future surveys will probably reveal that southern migrants are more common in the region than previously supposed. Acknowledgements We thank Dr D. Causey for facilities to examine the specimens in MCZ. J. Cooper and G. M. Kirwan greatly improved the final manuscript, and S. Kenney, G. D. Bieber, and J. P. Coimbra kindly commented on earlier versions. Branyl Com. & Ind. Téxtil Ltda partially supported the studies of C. J. Carlos. C. E. Fedrizzi received a master’s scholarship from the Fundagao Coordenacao de Aperfeigoamento de Pessoal de Nivel Superior (CAPES), Brasilia, Brazil. References: Antas, P. de T. Z. 1991. Status and conservation of seabirds in Brazilian waters. Pp. 140-158 in Croxall, J. P. (ed.) Seabird status and conservation: a supplement. International Council for Bird Preservation, Cambridge, UK. Azevedo Junior, S. M. 1998. As aves do Canal de Santa Cruz, Pernambuco, Brazil. Cad. Omega Univ. Fed. Rural de Pernambuco, Sér. Biol. 5: 35-50. Blake, E. R. 1977. Manual of Neotropical birds, vol. 1. Chicago Univ. Press. Harrison, P. 1983. Seabirds: an identification guide. Croom Helm, Beckenham. del Hoyo, J. Elliott, A. & Sargatal, J. (eds.) 1992. Handbook of the birds of the world, vol. 1. Lynx Edicions, Barcelona. Novaes, F. C. 1959. Procellaria aequinoctialis on Amazon River in Brazil. Condor 61: 299. Olmos, F., Martuscelli, P., Silva e Silva, R. & Neves, T. 1995. The seabirds of Sao Paulo, southeastern Brazil. Bull. Brit. Orn. Cl. 115: 117-128. Paynter, R. A. & Traylor, M. A. 1991. Ornithological gazetteer of Brazil, vol. 2. Mus. Comp. Zool., Harvard Univ., Cambridge, MA. Pinto, O. M. O. 1978. Novo catdlogo das aves do Brasil, 1* parte: aves nado Passeriformes e Passeriformes nado Oscines com exclusdo da familia Tyrannidae. Empresa Grafica da Revista dos Tribunais S.A., Sao Paulo. Sampaio, C. L. S. & Castro, J. O. 1998. Registro de Phoebetria palpebrata (Foster, 1785) no litoral da Bahia, nordeste do Brasil (Procellariformes: Diomedidae). Ararajuba 6: 136-137. Sick, H. 1997. Ornitologia brasileira. Ed. Nova Fronteira, Rio de Janeiro. Carlos et al. 290 Bull. B.O.C. 2004 124(4) Souza, M. C. 1993. Sobre aves marinhas no litoral do estado de Sergipe e Alagoas. Jn IIT Congresso Brasileiro de Ornitologia. Resumos. Universidade Catélica de Pelotas/Sociedade Brasileira de Ornitologia, Pelotas. Telino Junior, W. R., Lyra-Neves, R. M., Farias, G. B., Brito, M. T., Pacheco, G. & Oliveira-Siqueira, S. A. 2001. Ocorréncia e aspectos comportamentais da pomba-antartica, Chionis alba (Charadriiformes: Chionidae), em Pernambuco, Brasil. Tangara 1: 26-29. Teixeira, D. M., Oren, D. C. & Best, R. C. 1986. Notes on some Brazilian seabirds (2). Bull. Brit. Orn. Cl. 106: 74-77. Vooren, C. M. & Brusque, L. F. 1999. Diagnéstico sobre aves do ambiente costeiro no Brasil. Report to the Programa Nacional da _ Diversidade Bioldgica (PRONABIO). Available: http://www.bdt.org.br/workshop/costa/aves. Addresses: Caio José Carlos (author for correspondence), Programa de P6s-Graduacao em Oceanografia Biolégica, Fundagao Universidade Federal do Rio Grande, Av. Italia Km 8, C.P. 474, Rio Grande, RS 96201-900, Brazil, e-mail: cajoca@uol.com.br. Jeremiah Trimble, Bird Department, Museum of Comparative Zoology, Harvard University, 26 Oxford Street, Cambridge, MA 02138, USA, e-mail: jtrimble @ oeb.harvard.edu. Carmem Elisa Fedrizzi, Mestrado de Biologia Animal, Departamento de Zoologia, Universidade Federal de Pernambuco, Av. Professor Moraes Rego 1235, Cidade Universitaria, Recife, PE 50670-420, Brazil; current address: Programa de Pés-Graduagao em Oceanografia Biol6gica, Fundacgao Universidade Federal do Rio Grande, Av. Italia Km 8, C.P. 474, Rio Grande, RS 96201-900, Brazil, e-mail: cefedrizzi@uol.com.br. © British Ornithologists’ Club 2004 Motacilla samveasnae is the correct scientific name for the Mekong Wagtail by 7 W Duckworth & Per Alstrém Received 23 March 2004 The Mekong Wagtail Motacilla samveasnae was described recently (Duckworth et al. 2001). The spelling of its name was questioned by van Rootselaar (2002), who stated that ‘Following the nomenclatural rules of the International Commission on Zoological Nomenclature...and considering that the species’ name was ‘formed directly from a modern personal name’ and that ‘the name is to be formed by adding to the stem of that name -i if the personal name is that of a man’, the Mekong Wagtail’s scientific name should perhaps be cited as ‘Motacilla samveasnai Duckworth et al. 2001’, instead of Motacilla samveasnae’. This proposal is not correct, and would lead to confusion if adopted. The International code of zoological nomenclature, fourth edn (International Commission on Zoological Nomenclature 1999) governs the formation and usage of all names proposed on or after 1 January 2000. Article 31.1.1 states that “A species group name, if a noun in the genitive case formed from a personal name that is Latin, or from a modern personal name that is or has been Latinized, is to be J. W. Duckworth & Per Alstrém 291 Bull. B.O.C. 2004 124(4) formed in accordance with the rules of Latin grammar’. Article 31.1.2 states that ‘A species group name, if a noun in the genitive case...formed directly from a modern personal name, is to be formed by adding to the stem of that name -/ if the personal name is that of a man.,... -ae if of a woman...’. Those proposing names are at liberty whether to follow article 31.1.1 or 31.1.2. The bird is named after Sam Veasna, a man (Poole 2000), and therefore under article 31.1.2 it would take the form ‘samveasnai , aS suggested by van Rootselaar. However, the masculine genitive singular ending -ai may not have existed in Classical Latin (if it did, it was very rare), the genitive singular of Latin nouns (of either gender) ending in -a typically being -ae (e.g. agricola, -ae, masculine, a farmer). Proposing the name under article 31.1.1 avoids the awkward ‘ai’ ending. As a personal name ‘samveasna’ is a noun. In treating its genitive as ‘samveasnae’ it was Latinized in accordance with the rules of Latin grammar. The present example is thus analogous to that presented under article 31.1.1, whereby a man’s name, “Poda’, is also used directly, and given the genitive form of ‘podae’. This style has typically been used for species-group names where the man’s name ends in -a, e.g. Turdus feae and Muntiacus feae, both named after Leonardo Fea, the (male) Italian ornithologist and collector. The code makes it clear that the spelling ‘samveasnae’ should be retained unchanged. Article 32.1 defines ‘the ‘original spelling’ of a name as the spelling used in the work in which the name was established’ (in this case, Duckworth et al. (2001), who used ‘samveasnae’). Article 32.2 states that ‘the original spelling of a name is the ‘correct original spelling’, unless it is demonstrably incorrect as provided in Article 32.5’. Article 32.5 defines incorrect original spellings. Article 32.5.2 deals with presentational issues (diacritics, ligatures, apostrophes, hyphens etc.) and article 32.5.3 refers only to family-group names. The only part of article 32.5 relevant to Motacilla samveasnae is article 32.5.1, which states, “if there is in the original publication itself, without recourse to any external source of informa- tion, clear evidence of an inadvertent error...it must be corrected.” Nowhere in Duckworth ef al. (2001) did we state or imply that article 31.1.2 was used in forming the name (this was an assumption by van Rootselaar), nor did we state that Sam Veasna was a man. Thus, there are no grounds for considering ‘“samveasnae’ an incorrect original spelling as defined by the code. Article 32.3 specifies that ‘the correct original spelling of a name is to be preserved unaltered, except where it is mandatory to change the suffix or the gender ending under Article 34’. No provision of article 34 is relevant to this case: all deal with ‘mandatory changes in spelling consequent upon changes in rank or combina- tion’. Hence, no article in the code supports van Rootselaar’s statement that the original spelling should be changed. Because this is a complex issue, the code provides specific guidance through article 31.1.3: “The original spelling of a name J. W. Duckworth & Per Alstrém 292 Bull. B.O.C. 2004 124(4) formed under Articles 31.1.1 and ... [see above] is to be preserved unless it is incorrect [Arts. 32.3, 32.4]’ (see above). Acknowledgements We thank Nigel Collar for drawing our attention to van Rootselaar’s statement, and Walter Bock, Douglas Brandon-Jones, Normand David, Edward Dickinson, Colin Groves, Peter Grubb and Colin Poole for advice on the issue. References: Duckworth, J. W., Alstr6m, P., Davidson, P., Evans, T. D., Poole, C. M., Tan Setha & Timmins, R. J. 2001. A new species of wagtail from the lower Mekong basin. Bull. Brit. Orn. Cl. 121: 152-182. International Commission on Zoological Nomenclature 1999. International code of zoological nomen- clature. Fourth edn. The International Trust for Zoological Nomenclature, The Natural History Museum, London. Poole, C. 2000. Obituary: Sam Veasna. Oriental Bird Club Bull. 31: 8. van Rootselaar, O. 2002. New birds for the world: species described during 1999-2002. Birding World 15: 428-431. Addresses: J. W. Duckworth, East Redham Farm, Pilning, Bristol BS35 4JG UK. Per Alstrém, Department of Systematic Zoology, Evolutionary Biology Centre, Uppsala University, Norbyvagen 18 D, SE-752 36 Uppsala, Sweden, e-mail: per.alstrom @ebc.uu.se © British Ornithologists’ Club 2004 The above contribution raises an interesting issue, of which future contributors of papers describing new taxa, or proposing new names for existing taxa, need to be mindful. Both the etymologies of English and scientific names, and their derivations, should be clearly explained in all such cases. In the present instance, the authors of the new wagtail, Motacilla samveasnae, have successfully demonstrated that their original name was correct, but a clear explanation of the derivation of their suffix in the original publication would have avoided the need for such clarification —THE EDITOR. MEMBERSHIP See also website: http://www.boc-online.org Subscription rates will increase on 1 January 2005 as below: BOU Members £17.50 (US$36.00) Non-BOU Members £24.00 (US$48.00) All paid-up Members of the Club receive (postage free) four quarterly issues of the Bulletin, and the annual index. New Members are welcomed, at any time. CORRESPONDENCE Correspondence on all general Club matters should be addressed to: The Hon. Secretary, S.A.H. (Tony) Statham, Woodcock Hill, Durrants Lane, Berkhamsted, Herts. HP4 3TR, UK (or e-mail: SAHS @tinyonline.co.uk). For details of Club Meetings see inside front cover. 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Publications Officer BOC, Natural Resources Institute, University of Greenwich at Medway, Central Avenue, Chatham Maritime, Chatham, Kent ME4 4TB (e-mail: r.a.cheke @ greenwich.ac.uk) PAYMENTS All amounts quoted are net and should be paid in £ sterling, if possible. Payments in other currencies must include a further £4 for UK bank charges (except for annual rates in US dollars, which are inclusive). All cheques or drafts should be made payable to the British Ornithologists’ Club. If preferred, remittances may be made by bank transfer direct to the Club’s bank account: Barclays Prime Account, Dale House, Wavertree Boulevard, Liverpool L7 9PQ, UK. (Sort Code 20-00-87 Account No. 10211540), with confirmation to the Hon. Treasurer, D.J. Montier, Eyebrook, Oldfield Road, Bickley, Bromley, Kent BR1 2LF. COMMITTEE Dr C.F. Mann (Chairman) (2001) Cdr. M.B. Casement OBE RN (Vice-Chairman & Membership Secretary (2004) S.A.H. Statham (Hon. Secretary) (2004) D.J. Montier (Hon. Treasurer) (1997) | I.R. Bishop OBE (2003) Dr P.G.W. Salaman (Hon. Website Manager) (2001) C.W.R. Storey (2003) Prof. R.A. Cheke (BOC Publications) (2001) J.P. Hume (2004) Ex-officio members Hon. Editor: GM. Kirwan (1 January 2004) Chairman of BOU/BOC Joint Publications Committee (JPC): Reverend T.W. Gladwin. SONIAN INSTITUTION LIB Bulletin of the British Ornitho Wil Edited by Guy M. Kirw 117 9587 Volume 124, Number 4, pages ae CONTENTS KRABBE, N. A record of Pale-legged Hornero Furnarius leucopus from Ecuador ............. KIRWAN, G M. A Syrian record: the case of Aharoni's Thick-billed Larks Ramphocoris clotbey . . TAYLOR, B., WONDAFRASH, M. & DEMEKE, Y. The nest, eggs and chicks of the White-winged Flufftail Sarothrura ayresi. «os << ed iw ee ee ee kn we 2 233 WHITTAKER, A. Noteworthy ornithological records from Rond6nia, Brazil, including a first country record, comments on austral migration, life history, taxonomy and distribution, with relevant data from neighbouring states, and a first record for Bolivia..................... 239 CABOT, J. & DE VRIES, T. Age- and sex-differentiated plumages in the two colour morphs of the Variable Buzzard Buteo polyosoma: a case of delayed maturation with subadult males disguised in definitive adult female plumage ........-..... 20... -0e00e0s++ 05) oe 272 WHITTAKER, A. & CARLOS, B. Recent observations of Dull-coloured Grassquit Tiaris obscura in Mato Grosso reinforce its status as an austral migrant to south-west Brazil .............. 285 CARLOS, C. J., TRIMBLE, J. & FEDRIZZI, C. E. A specimen of Cape Petrel Daption capense from north-east Brazil .. 2... ke be cee eee eect bee ee eee ese sas 3 287 DUCKWORTH, J. W. & ALSTROM, P. Motacilla samveasnae is the correct scientific name for the Mekong Wagtail . . 20.25.86 0c eee eves bok e eee anes an bs 0 2 gee eee 290 Authors are invited to submit papers on topics relating to the broad themes of taxonomy and distribution of birds. Descriptions of new species of birds are especially welcome and will be given priority to ensure rapid publication, subject to successful passage through the normal peer review procedure, and they may be accompanied by colour photographs or paintings. On submission, manuscripts, double-spaced and with wide margins, should be sent to the Editor, Guy Kirwan, preferably by e-mail, to GMKirwan@aol.com. Alternatively, two copies of manuscripts, typed on one side of the paper, may be submitted to the Editor, 74 Waddington Street, Norwich NR2 4JS, UK. Where appropriate half-tone photographs may be included and, where essential to illustrate important points, the Editor will consider the inclusion of colour figures (if pos- sible, authors should obtain funding to support the inclusion of such colour illustrations). As far as possible, review, return of manuscripts for revision and subsequent stages of the publication process will be undertaken electronically. For instructions on style, see the inside rear cover of Bulletin 124 (1) or the BOC website: www.boc-online.org ©British Ornithologists’ Club 2004 Apart from single copies made for the purposes of research or private study, or criticism or review, as per- mitted under UK law, no part of this publication may be reproduced, stored or transmitted in any form or by any means, except with prior permission of the publishers. Enquiries concerning reproduction outside these terms should be sent to the Editor; for address see inside rear cover. The Bulletin is despatched from the printer on publication and is sent by Surface Saver Postal Services to all European destinations outside the UK and by Air Saver Postal Services to destinations outside Europe. Those whose subscriptions have not been received by the beginning of a month of publication will have their copies despatched by surface mail, after their current subscription has been paid. Printed on acid-free paper. Published by the British Ornithologists’ Club Typeset by Alcedo Publishing of Pennsylvania, USA, and printed by Crowes of Norwich, UK | xg Bulletin of the ae j : Alip e } wey 05 2005 LIBRARIES ee Edited by Guy Kirwan Index for Volume 124 (2004) Compiled by Mary N. Muller il LIST OF AUTHORS AND CONTENTS ALSTROM, P. see DUCKWORTH, J. W. ANGEHR, G. R., CHRISTIAN, D. G. & APARICIO, K. M. A survey of the Serrania de Jungurud6, an isolated mountain range in eastern Pamama................cssccesceeeseeeenceesseeeecesseesseeensees ANTOINE-FEILL S., A. H. see WHITTAKER, A. APARICIO, K. M. see ANGEHR, G. R. BELFORT GOMES, H. see RODRIGUES, M. BRAIMAH, J. see MARKS, B. D. BRAYSHAW, M. see YOUNG, H. G. BRIED, J. & MAGALHAES, M. C. First Palearctic record of the endangered Bermuda Petrel PLCKOAVOING CANOW sevcscacisscesvsedcssscsinssnnvscetepentesees Meenossonnt and oe ete BRUCE, M. D. & DOWSETT, R. J. The correct name of the Afrotropical mainland subspecies of Barn: Ow Tito) QI Dd 2s... asc csnsw ss casentececeeooncannsehoncinu'ee Ong, Ose e eon coon EE oreo RE nee eer BUCKLEY, F. G. sce BUCKLEY, FP. A. BUCKLEY, P. A. & BUCKLEY, F. G. Rapid speciation by a Lesser Antillean endemic, Barbados Bullfineh Loxigilla bar badensis. ...0.000:...cs0ssssecessecssouvereeonnoodeestskesoeeeetsectieies oe CABOT, J. & VRIES, T. de. Age- and sex-differentiated plumages in the two colour morphs of the Variable Buzzard Buteo polyosoma: a case of delayed maturation with subadult males disguised in definitive adult female plumage...............<.<.--<.+-se0c:.c+-<0c<-s2s---=-2< CARLOS, B. see WHITTAKER, A. CARLOS, C. J., TRIMBLE, J. & FEDRIZZI, C. E. A specimen of Cape Petrel Daption capense from north-east Brazil ..scs.0c.4-secass.ccesscceceencescoceusese cost son sntce sa cncdemeseunedtcescodetesoe ete eee ee CHAVES, JOAS sce PREILESY P- CHRISTIAN, D. G. see ANGEHR, G. R. CLEERE, N. A previously unidentified museum specimen of Plain-tailed Nighthawk Nyctiprogne vielliardi-(Caprimul 21dae)..........sos..de..+0.steececes eeneesencte cata -Bericene seg eedes teatecc-+ ie CLUB NOTICES Notice and Agenda for the AGM 27 April 2004 ............<.s..csecsccecossses0sse-2eecece- 02s Report of the AGM held on 27 April 2004 ...... ... -2.0.0...