SEABIRDS RECORDED at the CHATHAM ISLANDS, 1960 to MAY 1993 by M.J
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Copulation and Mate Guarding in the Northern Fulmar
COPULATION AND MATE GUARDING IN THE NORTHERN FULMAR SCOTT A. HATCH Museumof VertebrateZoology, University of California,Berkeley, California 94720 USA and AlaskaFish and WildlifeResearch Center, U.S. Fish and WildlifeService, 1011 East Tudor Road, Anchorage,Alaska 99503 USA• ABSTRACT.--Istudied the timing and frequency of copulation in mated pairs and the occurrenceof extra-paircopulation (EPC) among Northern Fulmars (Fulmarus glacialis) for 2 yr. Copulationpeaked 24 days before laying, a few daysbefore females departed on a prelaying exodus of about 3 weeks. I estimated that females were inseminated at least 34 times each season.A total of 44 EPC attemptswas seen,9 (20%)of which apparentlyresulted in insem- ination.Five successful EPCs were solicitated by femalesvisiting neighboring males. Multiple copulationsduring a singlemounting were rare within pairsbut occurredin nearly half of the successfulEPCs. Both sexesvisited neighborsduring the prelayingperiod, and males employed a specialbehavioral display to gain acceptanceby unattended females.Males investedtime in nest-siteattendance during the prelaying period to guard their matesand pursueEPC. However, the occurrenceof EPC in fulmars waslargely a matter of female choice. Received29 September1986, accepted 16 February1987. THEoccurrence and significanceof extra-pair Bjorkland and Westman 1983; Buitron 1983; copulation (EPC) in monogamousbirds has Birkhead et al. 1985). generated much interest and discussion(Glad- I attemptedto documentthe occurrenceand stone 1979; Oring 1982; Ford 1983; McKinney behavioral contextof extra-pair copulationand et al. 1983, 1984). Becausethe males of monog- mate guarding in a colonial seabird,the North- amous species typically make a large invest- ern Fulmar (Fulmarus glacialis). Fulmars are ment in the careof eggsand young, the costof among the longest-lived birds known, and fi- being cuckolded is high, as are the benefits to delity to the same mate and nest site between the successfulcuckolder. -
Chatham Island and Pitt Island Shag Census 2011 DRAFT REPORT
MCSPOP2010-02 DRAFT REPORT MCSPOP2010-02: Chatham Island and Pitt Island shag census 2011 DRAFT REPORT Chatham Island shag Pitt Island shag May 2012 Igor Debski1, Mike Bell2 and Dan Palmer1 1Science and Technical Group, Department of Conservation, PO Box 10-420, Wellington 6143 2Wildlife Management International Limited, PO Box 45, Spring Creek, Marlborough 7244 1 MCSPOP2010-02 DRAFT REPORT Abstract We conducted an extensive survey of coastal areas suitable for Chatham Island and Pitt Island shag nesting between August and November 2011. The census methods were designed to maximise comparability with an earlier census in 1997/98. Based on a complete census of all known Chatham Island shag breeding colonies we estimated the breeding population to be 355 pairs, representing a 58 % decline since 1997/98. We estimated the total Pitt Island shag breeding population to be 434 pairs, a 40% decline since 1997/98 (extrapolated numbers were used for some outlying islands known to hold this species that we did not visit). A series of regular observations showed that breeding activity for both species peaks in October, though there is some notable variation in timing between colonies. Such variation must be taken into consideration in estimating the total breeding population for both species. Both species are distributed across the Chatham Islands group. We found that population declines since 1997/98 have been particularly steep for both species at Pitt Island and outlying islands, with smaller declines on main Chatham Island. A range of anthropogenic threats have been identified, both land-based and at-sea. Because population declines have been particularly pronounced at pest-free, protected out-lying islands we conclude that at-sea factors are likely to be driving the population decline, though more research is required to identify causal factors. -
Fledging Behaviour of Juvenile Northern Royal Albatrosses (Diomedea Sanfordi): a GPS Tracking Study
135 Notornis, 2010, Vol. 57: 135-147 0029-4470 © The Ornithological Society of New Zealand, Inc. Fledging behaviour of juvenile northern royal albatrosses (Diomedea sanfordi): a GPS tracking study BindI Thomas* Edward O. Minot John d. Holland Institute of Natural Resources, massey University, Private Bag 11-222, Palmerston North, New Zealand Abstract Using GPS technology, we tracked 3 juvenile northern royal albatrosses (Diomedea sanfordi) as they fledged from Taiaroa Head, Otago Peninsula, New Zealand. All birds flew north along the east coast of New Zealand before undertaking a trans-Pacific easterly migration to Chile. during their 8500 km migration, the maximum daily distance and speed reached were 1047 km and 110 km h-1, respectively, and the maximum altitude was 38 m a.s.l. Upon leaving New Zealand waters, the 3 albatrosses took between 16 to 34 days to reach the coast of Chile where they remained between 23°S and 58°S. The tracked albatrosses generally kept to within 100 km of the coast where the depth of water varied between 1000 and 2000 m. Overall, the tracked albatrosses on the Chilean coast spent 72% of the time resting on the water, primarily between 1800 h and 2400 h local time. Fix success rate of the GPS technology ranged from 56% to 85%. The use of solar charging and a long attachment period allowed birds to be followed continuously for 134 to 362 days. Our study confirms the value of GPS technology in uncovering the movements and life history of wide-ranging oceanic birds. Thomas, B.; minot, E.O.; Holland, J.d. -
The Taxonomy of the Procellariiformes Has Been Proposed from Various Approaches
山 階 鳥 研 報(J. Yamashina Inst. Ornithol.),22:114-23,1990 Genetic Divergence and Relationships in Fifteen Species of Procellariiformes Nagahisa Kuroda*, Ryozo Kakizawa* and Masayoshi Watada** Abstract The genetic analysis of 23 protein loci in 15 species of Procellariiformes was made The genetic distancesbetween the specieswas calculatedand a dendrogram was formulated of the group. The separation of Hydrobatidae from all other taxa including Diomedeidae agrees with other precedent works. The resultsof the present study support the basic Procellariidclassification system. However, two points stillneed further study. The firstpoint is that Fulmarus diverged earlier from the Procellariidsthan did the Diomedeidae. The second point is the position of Puffinuspacificus which appears more closely related to the Pterodroma petrels than to other Puffinus species. These points are discussed. Introduction The taxonomy of the Procellariiformes has been proposed from various approaches. The earliest study by Forbes (1882) was made by appendicular myology. Godman (1906) and Loomis (1918) studied this group from a morphological point of view. The taxonomy of the Procellariiformes by functional osteology and appendicular myology was studied by Kuroda (1954, 1983) and Klemm (1969), The results of the various studies agreed in proposing four families of Procellariiformes: Diomedeidae, Procellariidae, Hydrobatidae, and Pelecanoididae. They also pointed out that the Procellariidae was a heterogenous group among them. Timmermann (1958) found the parallel evolution of mallophaga and their hosts in Procellariiformes. Recently, electrophoretical studies have been made on the Procellariiformes. Harper (1978) found different patterns of the electromorph among the families. Bar- rowclough et al. (1981) studied genetic differentiation among 12 species of Procellari- iformes at 16 loci, and discussed the genetic distances among the taxa but with no consideration of their phylogenetic relationships. -
NSW Vagrant Bird Review
an atlas of the birds of new south wales and the australian capital territory Vagrant Species Ian A.W. McAllan & David J. James The species listed here are those that have been found on very few occasions (usually less than 20 times) in NSW and the ACT, and are not known to have bred here. Species that have been recorded breeding in NSW are included in the Species Accounts sections of the three volumes, even if they have been recorded in the Atlas area less than 20 times. In determining the number of records of a species, when several birds are recorded in a short period together, or whether alive or dead, these are here referred to as a ‘set’ of records. The cut-off date for vagrant records and reports is 31 December 2019. As with the rest of the Atlas, the area covered in this account includes marine waters east from the NSW coast to 160°E. This is approximately 865 km east of the coast at its widest extent in the south of the State. The New South Wales-Queensland border lies at about 28°08’S at the coast, following the centre of Border Street through Coolangatta and Tweed Heads to Point Danger (Anon. 2001a). This means that the Britannia Seamounts, where many rare seabirds have been recorded on extended pelagic trips from Southport, Queensland, are east of the NSW coast and therefore in NSW and the Atlas area. Conversely, the lookout at Point Danger is to the north of the actual Point and in Queensland but looks over both NSW and Queensland marine waters. -
Bugoni 2008 Phd Thesis
ECOLOGY AND CONSERVATION OF ALBATROSSES AND PETRELS AT SEA OFF BRAZIL Leandro Bugoni Thesis submitted in fulfillment of the requirements for the degree of Doctor of Philosophy, at the Institute of Biomedical and Life Sciences, University of Glasgow. July 2008 DECLARATION I declare that the work described in this thesis has been conducted independently by myself under he supervision of Professor Robert W. Furness, except where specifically acknowledged, and has not been submitted for any other degree. This study was carried out according to permits No. 0128931BR, No. 203/2006, No. 02001.005981/2005, No. 023/2006, No. 040/2006 and No. 1282/1, all granted by the Brazilian Environmental Agency (IBAMA), and International Animal Health Certificate No. 0975-06, issued by the Brazilian Government. The Scottish Executive - Rural Affairs Directorate provided the permit POAO 2007/91 to import samples into Scotland. 2 ACKNOWLEDGEMENTS I was very lucky in having Prof. Bob Furness as my supervisor. He has been very supportive since before I had arrived in Glasgow, greatly encouraged me in new initiatives I constantly brought him (and still bring), gave me the freedom I needed and reviewed chapters astonishingly fast. It was a very productive professional relationship for which I express my gratitude. Thanks are also due to Rona McGill who did a great job in analyzing stable isotopes and teaching me about mass spectrometry and isotopes. Kate Griffiths was superb in sexing birds and explaining molecular methods again and again. Many people contributed to the original project with comments, suggestions for the chapters, providing samples or unpublished information, identifyiyng fish and squids, reviewing parts of the thesis or helping in analysing samples or data. -
Southern Fulmar
SOUTHERN FULMAR Fulmarus glacialoides Document made by the French Southern and Antarctic Lands © TAAF Lands © Southern and Antarctic the French made by Document l l assessm iona asse a g ss b e e m lo n r • Size : 45-50 cm t F G e A n t A SOUTHERN FULMAR T • Wingspan : 114-120 cm Fulmarus glacialoides • Weight : 0.7-1kg Order : Procellariiformes — Family : Procellariidae as the ... It is also known GEOGRAPHIC RANGE : The species can be seen in the Southern Ocean but breeds on the coasts of Antarctica and outlying glaciated islands. HABITAT : Southern Fulmars nest on steep rocky slopes and cliff sides, mainly on the coast and on the Antarctic continent. They are highly nomadic outside the breeding season, generally moving north to open waters south of 30°S. © S. BLANC DIET : They eat krill, fish and squid depending on available prey. They also consume carrion and discards from Fulmar Antarctic fishing vessels. BEHAVIOR : REPRODUCTION : Most food is taken by surface-seizing whilst in The breeding season begins in November and egg- flocks. They also skim the surface in low flight laying takes place during the first two weeks of with their beak open. They also sometimes dive December. They breed in colonies on steep rocky at shallow depths to catch their prey. They are slopes and precipitous cliffs on sheltered ledges rather solitary birds that can form small groups or in hollows, sometimes with other species of outside the breeding season. Paired birds tend to petrels. Nests are a gravel-lined scrape in which © S. -
Onetouch 4.0 Scanned Documents
/ Chapter 2 THE FOSSIL RECORD OF BIRDS Storrs L. Olson Department of Vertebrate Zoology National Museum of Natural History Smithsonian Institution Washington, DC. I. Introduction 80 II. Archaeopteryx 85 III. Early Cretaceous Birds 87 IV. Hesperornithiformes 89 V. Ichthyornithiformes 91 VI. Other Mesozojc Birds 92 VII. Paleognathous Birds 96 A. The Problem of the Origins of Paleognathous Birds 96 B. The Fossil Record of Paleognathous Birds 104 VIII. The "Basal" Land Bird Assemblage 107 A. Opisthocomidae 109 B. Musophagidae 109 C. Cuculidae HO D. Falconidae HI E. Sagittariidae 112 F. Accipitridae 112 G. Pandionidae 114 H. Galliformes 114 1. Family Incertae Sedis Turnicidae 119 J. Columbiformes 119 K. Psittaciforines 120 L. Family Incertae Sedis Zygodactylidae 121 IX. The "Higher" Land Bird Assemblage 122 A. Coliiformes 124 B. Coraciiformes (Including Trogonidae and Galbulae) 124 C. Strigiformes 129 D. Caprimulgiformes 132 E. Apodiformes 134 F. Family Incertae Sedis Trochilidae 135 G. Order Incertae Sedis Bucerotiformes (Including Upupae) 136 H. Piciformes 138 I. Passeriformes 139 X. The Water Bird Assemblage 141 A. Gruiformes 142 B. Family Incertae Sedis Ardeidae 165 79 Avian Biology, Vol. Vlll ISBN 0-12-249408-3 80 STORES L. OLSON C. Family Incertae Sedis Podicipedidae 168 D. Charadriiformes 169 E. Anseriformes 186 F. Ciconiiformes 188 G. Pelecaniformes 192 H. Procellariiformes 208 I. Gaviiformes 212 J. Sphenisciformes 217 XI. Conclusion 217 References 218 I. Introduction Avian paleontology has long been a poor stepsister to its mammalian counterpart, a fact that may be attributed in some measure to an insufRcien- cy of qualified workers and to the absence in birds of heterodont teeth, on which the greater proportion of the fossil record of mammals is founded. -
Evaluating Threats to New Zealand Seabirds Report for the Department of Conservation
Evaluating threats to New Zealand seabirds Report for the Department of Conservation Authors: Edward Abraham Yvan Richard Katherine Clements PO Box 27535, Wellington 6141 New Zealand dragonfly.co.nz Cover Notes To be cited as: Abraham, Edward; Yvan Richard; Katherine Clements (2016). Evaluating threats to New Zealand seabirds, 19 pages. Report for the Department of Conservation. Crown copyright © This report is licensed for re-use under a Creative Commons Aribution 3.0 New Zealand Licence. This allows you to distribute, use, and build upon this work, provided credit is given to the original source. Cover image: hps://www.flickr.com/photos/4nitsirk/16121373851 EXECUTIVE SUMMARY The New Zealand Department of Conservation is developing a seabird threat framework, “to beer understand, and manage, at-sea threats to our seabirds”. This framework will allow the impact of threats on seabird populations to be qualitatively assessed, and will be used to prioritise a programme of seabird population monitoring. As a first stage in developing the framework, a database of demographic parameters and threats was prepared. In this project, a process was estab- lished for reviewing and synthesising this information. The demographic parameters were then used to develop an online tool, which allowed for the impact of changes in parameters on population growth rates to be assessed. In the future, this tool will allow the impact of current and potential threats on seabird populations to be promptly explored. The process was trialled on the 12 albatross taxa recognised -
Chatham Island Shag Census 2014-2016
Chatham Island shag census 2014-2016 1 Chatham Island shag census 2014-2016 Mike Bell, Dave Bell, Dave Boyle and Hamish Tuanui-Chisholm. Wildlife Management International Ltd PO Box 607 Blenheim 7240 New Zealand www.wmil.co.nz Chatham Island Taiko Trust PO Box 2 Chatham Island 8942 www.taiko.org.nz This report was prepared by Wildlife Management International Limited and the Chatham Island Taiko Trust for the Department of Conservation as partial fulfilment of the contract POP2016-01 Seabird Population research: Chatham Islands 2016-17 dated October 2016. June 2017 Citation: This report should be cited as: Bell, M.D.; Bell, D.J.; Boyle, D.P.; Tuanui-Chisholm, H. 2017. Chatham Island Shag census 2014-2016. Technical report to the Department of Conservation. All photographs in this Report are copyright © WMIL unless otherwise credited, in which case the person or organization credited is the copyright holder. EXECUTIVE SUMMARY Annual aerial surveys to count the breeding population of Chatham Island shags were carried out during the 2014, 2015 and 2016 breeding seasons. Each season two aerial surveys of all colonies were undertaken, with an additional early flight in 2016 to count the colonies in Te Whanga Lagoon. The number of Chatham Island shags was estimated at 856 breeding pairs, found in 13 breeding colonies. This result is very similar to that recorded in 1997 (842 pairs) but significantly higher than counts from 2003 and 2011. Methodology was the same in the 1997 and 2014-2016 counts and suggest the Chatham Island shag population has been stable for the last 20 years. -
REVIEWS Edited by J
REVIEWS Edited by J. M. Penhallurick BOOKS A Field Guide to the Seabirds of Britain and the World by is consistent in the text (pp 264 - 5) but uses Fleshy-footed Gerald Tuck and Hermann Heinzel, 1978. London: Collins. (a bette~name) in the map (p. 270). Pp xxviii + 292, b. & w. ills.?. 56-, col. pll2 +48, maps 314. 130 x 200 mm. B.25. Parslow does not use scientific names and his English A Field Guide to the Seabirds of Australia and the World by names follow the British custom of dropping the locally Gerald Tuck and Hermann Heinzel, 1980. London: Collins. superfluous adjectives, Thus his names are Leach's Storm- Pp xxviii + 276, b. & w. ills c. 56, col. pll2 + 48, maps 300. Petrel, with a hyphen, and Storm Petrel, without a hyphen; 130 x 200 mm. $A 19.95. and then the Fulmar, the Gannet, the Cormorant, the Shag, A Guide to Seabirds on the Ocean Routes by Gerald Tuck, the Kittiwake and the Puffin. On page 44 we find also 1980. London: Collins. Pp 144, b. & w. ills 58, maps 2. Storm Petrel but elsewhere Hydrobates pelagicus is called 130 x 200 mm. Approx. fi.50. the British Storm-Petrel. A fourth variation in names occurs on page xxv for Comparison of the first two of these books reveals a ridi- seabirds on the danger list of the Red Data Book, where culous discrepancy in price, which is about the only impor- Macgillivray's Petrel is a Pterodroma but on page 44 it is tant difference between them. -
BYC-08 INF J(A) ACAP: Update on the Conservation Status
INTER-AMERICAN TROPICAL TUNA COMMISSION SCIENTIFIC ADVISORY COMMITTEE NINTH MEETING La Jolla, California (USA) 14-18 May 2018 DOCUMENT BYC-08 INF J(a) UPDATE ON THE CONSERVATION STATUS, DISTRIBUTION AND PRIORITIES FOR ALBATROSSES AND LARGE PETRELS Agreement on the Conservation of Albatrosses and Petrels (ACAP) and BirdLife International 1. STATUS AND TRENDS OF ALBATROSSES AND PETRELS Seabirds are amongst the most globally-threatened of all groups of birds, and conservation issues specific to albatrosses and large petrels led to drafting of the multi-lateral Agreement on the Conservation of Albatrosses and Petrels (ACAP). A review of the conservation status and priorities for albatrosses and large petrels was recently published in Biological Conservation (Phillips et al. 2016). There are currently 31 species listed in Annex 1 of the Agreement. Of these, 21 (68%) are classified at risk of extinction, a stark contrast to the overall rate of 12% for the 10,694 bird species worldwide (Croxall et al. 2012, Gill & Donsker 2017). Of the 22 species of albatrosses listed by ACAP, three are listed as Critically Endangered (CR), six are Endangered (EN), six are Vulnerable (VU), six are Near Threatened (NT), and one is of Least Concern (LC). Of the nine petrel species, one is listed as CR, one as EN, four as VU, one as NT and two species as LC. The population trends of ACAP species over the last twenty years (since the mid-1990s) were re-examined in 2017 by the ACAP Population and Conservation Status Working Group (PaCSWG). Thirteen ACAP species (42%) are currently showing overall population declines.