Tectonic Collision and Uplift of Wallacea Triggered the Global Songbird Radiation
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New Zealand's Genetic Diversity
1.13 NEW ZEALAND’S GENETIC DIVERSITY NEW ZEALAND’S GENETIC DIVERSITY Dennis P. Gordon National Institute of Water and Atmospheric Research, Private Bag 14901, Kilbirnie, Wellington 6022, New Zealand ABSTRACT: The known genetic diversity represented by the New Zealand biota is reviewed and summarised, largely based on a recently published New Zealand inventory of biodiversity. All kingdoms and eukaryote phyla are covered, updated to refl ect the latest phylogenetic view of Eukaryota. The total known biota comprises a nominal 57 406 species (c. 48 640 described). Subtraction of the 4889 naturalised-alien species gives a biota of 52 517 native species. A minimum (the status of a number of the unnamed species is uncertain) of 27 380 (52%) of these species are endemic (cf. 26% for Fungi, 38% for all marine species, 46% for marine Animalia, 68% for all Animalia, 78% for vascular plants and 91% for terrestrial Animalia). In passing, examples are given both of the roles of the major taxa in providing ecosystem services and of the use of genetic resources in the New Zealand economy. Key words: Animalia, Chromista, freshwater, Fungi, genetic diversity, marine, New Zealand, Prokaryota, Protozoa, terrestrial. INTRODUCTION Article 10b of the CBD calls for signatories to ‘Adopt The original brief for this chapter was to review New Zealand’s measures relating to the use of biological resources [i.e. genetic genetic resources. The OECD defi nition of genetic resources resources] to avoid or minimize adverse impacts on biological is ‘genetic material of plants, animals or micro-organisms of diversity [e.g. genetic diversity]’ (my parentheses). -
Geckos on Australasia Side of Wallace Line Found to Be Growing to Twice the Size of Those in Asia 8 October 2014, by Bob Yirka
Geckos on Australasia side of Wallace Line found to be growing to twice the size of those in Asia 8 October 2014, by Bob Yirka impact of what has become known as the Wallace Line—bent toed geckos on the Australasia side are growing bigger than their Asian cousins, particularly on the island of New Guinea. The researchers looked at 87 species of the bent toed variety of the lizard out of 180 believed to live in the area, from both sides of the Line—using ancestral state analysis revealed that geckos living on New Guinea were evolving to grow to be approximately twice as long as their Asian counterparts—roughly 35cm. Though the cause for the apparent rise of gigantism in the lizards can't be proved as yet, the A dwarf yellow-headed gecko. Lygodactylus researchers strongly believe it's because the lizard luteopicturatus. Pictured in Dar es Salaam, Tanzania. has no predators on the island and because there App 7cm long. Credit: Wikipedia. is a nearly limitless supply of easy to obtain food. On New Guinea there are no mammals, and the largest carnivore is the marsupial Bronze Quoll, which grows to just 36cm. The researchers suggest A team made up of several researchers from that more research into the lineage of the lizard Australia and one from the U.S. has found that needs to be done to better understand their bent toed geckos living on the Australasia side of ecological shift—to find out if other causes might be The Wallace Line are evolving to grow up to twice at play as well. -
Disaggregation of Bird Families Listed on Cms Appendix Ii
Convention on the Conservation of Migratory Species of Wild Animals 2nd Meeting of the Sessional Committee of the CMS Scientific Council (ScC-SC2) Bonn, Germany, 10 – 14 July 2017 UNEP/CMS/ScC-SC2/Inf.3 DISAGGREGATION OF BIRD FAMILIES LISTED ON CMS APPENDIX II (Prepared by the Appointed Councillors for Birds) Summary: The first meeting of the Sessional Committee of the Scientific Council identified the adoption of a new standard reference for avian taxonomy as an opportunity to disaggregate the higher-level taxa listed on Appendix II and to identify those that are considered to be migratory species and that have an unfavourable conservation status. The current paper presents an initial analysis of the higher-level disaggregation using the Handbook of the Birds of the World/BirdLife International Illustrated Checklist of the Birds of the World Volumes 1 and 2 taxonomy, and identifies the challenges in completing the analysis to identify all of the migratory species and the corresponding Range States. The document has been prepared by the COP Appointed Scientific Councilors for Birds. This is a supplementary paper to COP document UNEP/CMS/COP12/Doc.25.3 on Taxonomy and Nomenclature UNEP/CMS/ScC-Sc2/Inf.3 DISAGGREGATION OF BIRD FAMILIES LISTED ON CMS APPENDIX II 1. Through Resolution 11.19, the Conference of Parties adopted as the standard reference for bird taxonomy and nomenclature for Non-Passerine species the Handbook of the Birds of the World/BirdLife International Illustrated Checklist of the Birds of the World, Volume 1: Non-Passerines, by Josep del Hoyo and Nigel J. Collar (2014); 2. -
The Species Flocks in the Ancient Lakes of Sulawesi, Indonesia
12 Aquatic biodiversity hotspots in Wallacea: the species fl ocks in the ancient lakes of Sulawesi, Indonesia T h o m a s v o n R i n t e l e n , K r i s t i n a v o n R i n t e l e n , M a t t h i a s G l a u b r e c h t , C h r i s t o p h D . S c h u b a r t a n d F a b i a n H e r d e r 12.1 Introduction Some of the world’s most spectacular species radiations or species fl ocks are found in so-called ‘ancient lakes’. Th ese are long-lived lakes that have existed for 100 000 years (Gorthner et al. 1994 , but see also Albrecht and Wilke 2008 ) or more (e.g. Lake Tanganyika and Lake Baikal). Ancient lakes are justifi ably regarded as hotspots of diversifi cation (e.g. Martens 1997 , Rossiter and Kawanabe 2000 ), even if not all ancient lake species fl ocks match the diversity of the super-fl ock of East African cichlids (e.g. Kornfi eld and Smith 2000 , Kocher 2004 ). Studies on the evo- lution of ancient lake organisms have continuously resulted in important insights into general patterns of speciation and radiation (e.g. Streelman and Danley 2003 ) ever since the seminal review of Brooks ( 1950 ). During the last decade, smaller ancient lakes (c. <1 000 km 2 ), which are generally less well investigated, have attracted increasing attention. -
Recovery of a Mohua (<Em Class="Sciname">Mohoua
Journal of the Ornithological Society of New Zealand ISSN 0029-4470 Recovery of a Mohua (Mohoua ochrocephala) population following predator control in the Eglinton Valley, Fiordland, New Zealand PETER DILKS Science C Research Unit, Department of Conservation, Private Bag, Christchurch ABSTRACT Breeding Mohua (Yellowhead, Mohoua ochrocephala; Passerifones) have been intensively monitored in the Eglinton Valley, Fiordland, since 1990. Birds were individually colour-banded and their territories mapped. Trapping and poisoning stoats (Mustela eninea) resulted in a large increase in Mohua numbers, but the population declined abruptly in winter 1996 following a period of unusually low temperatures. Details of the increase in numbers are presented and the reasons for the subsequent sharp population decline are discussed. KEYWORDS: Mohua, Yellowhead, Mohoua ochrocephala, stoat, Mustela erminea predation, hole nesting. INTRODUCTION The Mohua (Yellowhead,Mohoua ochrocephala) is a small, insectivorous, forest passerine, endemic to the South Island of New Zealand. In the last century Mohua were among the most abundant and conspicuous forest birds in the South Island, but they have all but disappeared from 75% of their former range since the arrival of Europeans and the introduction of mammalian predators (Gaze 1985). Mohua are now regarded as endangered (O'Donnell 1993). Monitoring has shown that Mohua suffer abrupt population declines during the stoat (Mustela erminea) irruptions that follow heavy beech (Nothofagus sp.) seeding (Elliott 1990, O'Donnell et al. 1996). Mohua are particularly vulnerable to stoats because they nest in holes, have long incubation and nestling periods, and breed in late spring, when stoat numbers are highest (Elliott 1990). The effect of stoat predation on the population is exacerbated by the fact that since only females incubate, most predation is on adult females (Elliott 1996a). -
<Em Class="Sciname">Mohoua Albicilla</Em>
Short Note 235 Moore, J.L. 1999. Norfolk Island bird notes, 1977 to 1997. Smart, J.B. 1973. Notes on the occurrence of waders in Notornis 46: 354-364. Fiji. Notornis 18: 267-279. Oliver, W.R.B. 1951. New Zealand birds. 2nd ed. Turbott, E.G. (convener). 1990. Checklist of the birds of New Wellington, A.H. & A.W. Reed. Zealand and the Ross Dependency, Antarctica. Auckland, Pierce, R.J. 1999. Regional patterns of migration in the Random Century New Zealand LtaJ. banded dotterel (Charadrius bicinctus bicinctus). Watling, D. 2001. Aguide to the birds of Fiji B western Polynesia. Notornis 46: 101-122. Suva, Fiji, Environmental Consu1tanl:s (Fiji) Ltd. Skinner, N.J. 1983. The occurrence of waders at Suva Keywords banded dotterel, Churadrius bicinctus, Point, Fiji. Notornis 30: 227-232. Vanuatu. Notornis, 2003, Vol. 50: 235 0029-4470 O The Ornithological Society of New Zealand, Inc. 2003 SHORT NOTE A longevity record for whitehead Mohoua albicilla, Pachycephalidae I. SOUTHEY 640 Waiuku Rd., R.D.3, Pukekohe, New Zealand. B.J. GILL Auckland Museum, Private Bag 92018, Auckland, New Zealand. On 22 January 2001, IS saw a colour-banded white- (1) Male B-41125, red/metal, red/white, banded as head (Mohoua albicilla) in the south-west of Little an adult in January 1985. Barrier Island near the main landing site. It was on (2) Male B-41131, red/metal, red/yellow, banded the flats, about 300 m east of the "Bunkhouse" and as a juvenile in March 1985. about 80 m from the shore. It had a metal band (M) The second bird would not have hatched after and 3 colour-bands in the combination red/metal January 1985. -
Biogeographical Modules and Island Roles: a Comparison of Wallacea
Journal of Biogeography (J. Biogeogr.) (2012) 39, 739–749 ORIGINAL Biogeographical modules and island ARTICLE roles: a comparison of Wallacea and the West Indies Daniel W. Carstensen1*, Bo Dalsgaard2,3, Jens-Christian Svenning4, Carsten Rahbek3, Jon Fjeldsa˚5, William J. Sutherland2 and Jens M. Olesen1 1Department of Bioscience, Aarhus University, ABSTRACT Ny Munkegade 114, DK-8000 Aarhus, Aim In order to advance our understanding of the assembly of communities on Denmark, 2Conservation Science Group, Department of Zoology, University of islands and to elucidate the function of different islands in creating regional and Cambridge, Downing Street, Cambridge CB2 subregional distribution patterns, we identify island biogeographical roles on the 3EJ, UK, 3Center for Macroecology, Evolution basis of the distribution of the islands’ biota within the archipelago. We explore and Climate, Department of Biology, which island characteristics determine island biogeographical roles. Furthermore, University of Copenhagen, Universitetsparken we identify biogeographical subregions, termed modules. 15, DK- 2100 Copenhagen, Denmark, Location Wallacea in Indonesia, and the West Indies in the Caribbean Sea. 4Ecoinformatics and Biodiversity Group, Department of Bioscience, Aarhus University, Methods We use a network approach to detect island biogeographical roles and Ny Munkegade 114, DK-8000 Aarhus, avian biogeographical modules. To designate the biogeographical role of an Denmark, 5Center for Macroecology, Evolution island, each island is assigned two coordinates, l and r. The position of an island and Climate, Natural History Museum of in l–r space characterizes its role, namely as peripheral, connector, module hub, Denmark, University of Copenhagen, DK-2100 or network hub. Island characteristics are tested as predictors of l and r. -
(2) Biodiversity in Sulawesi Island Wallacea Is a Famous And
Interim Report The Study on Arterial Road Network Development Plan for Sulawesi Island and Feasibility Study on Priority Arterial Road Development for South Sulawesi Province June 2007 (2) Biodiversity in Sulawesi Island Wallacea is a famous and essential biogeographical island group in eastern Indonesia which includes Sulawesi Island (which is about 178,700 km2). Sulawesi Island is the largest of these islands occupying about 53% of the island aggrupation located in the northwest part of Wallacea. Because of its tropical climate, its numerous islands, and complex geological history, Wallacea has high biodiversity, with numerous species found nowhere else in the world. Its total number of species is estimated at 11,400 and holds a high probability of undiscovered species due to the area’s isolation and inaccessibility. Table 9.4.1 Diversity and Endemism in Wallacea Taxonomic Endemic Percent Species Endemic Species (samples) Group Species Endemism Plants 10,000 1,500 15.0% babirusa, anoa, tarsiers, Mammals 222 127 57.2% kuskus, sulawesi palm civet, celebes black macaque etc. maleo, matinan flycatcher, white-tipped monarch, taliabu Birds 647 262 40.5% masked-owl, sulawesi red- knobbed hornbill etc. calamorhabdium, rabdion, Reptiles 222 99 44.6% cyclotyphlops etc. Amphibian sulawesi toad, green flog, 48 33 68.8% s common green turtle etc. Freshwater 250 50 20.0% halfbeak, goby, oryzia etc. Fishes 11,389 2,071 18.2% Threat Categories: CR = Critically Endangered; EN = Endangered; VU = Vulnerable; EW = Extinct in the Wild Endemism: Single = endemic to one hotspot; Multiple = not endemic to any one hotspot, but to the combined area of two or more hotspots 1) Plants Although the flora in this island region is not well known, it is estimated that there are about 10,000 species of vascular plants, with roughly 1,500 endemic species and at least 12 endemic genera. -
Best Practice Techniques for the Translocation of Whiteheads (Popokatea, Mohoua Albicilla)
Best practice techniques for the translocation of whiteheads (popokatea, Mohoua albicilla) Ralph Powlesland and Kevin Parker Cover: Whitehead, Tiritiri Matangi Island. Photo: Martin Sanders. © Copyright April 2014, New Zealand Department of Conservation Published by the Terrestrial Ecosystems Unit, National Office, Science and Capability Group, Department of Conservation, PO Box 10420, The Terrace, Wellington 6143, New Zealand. Editing and design by the Publishing Team, National Office, Department of Conservation, PO Box 10420, The Terrace, Wellington 6143, New Zealand. CONTENTS Abstract 1 1. Introduction 2 2. Animal welfare requirements 3 3. Transfer team 3 4. Time of year for transfer 3 5. Number of transfers 4 6. Composition of transfer group 4 7. Sexing whiteheads 4 7.1 Appearance 4 7.2 Measurements 5 7.3 DNA sexing 6 8. Ageing whiteheads 7 9. Capture 7 10. Transfer to base for ‘processing’ 7 11. Processing the birds 8 12. Temporary housing in aviaries 10 12.1 Capture in the aviary on transfer day 12 13. Feeding 14 14. Whitehead husbandry 15 15. Transfer box design 15 16. Transport 16 17. Release 17 18. Post-release monitoring 17 18.1 Purpose 17 18.2 Recommended monitoring 19 19. Record keeping 19 20. References 21 Appendix 1 Details of report contributors 23 Appendix 2 Feeding protocol for whiteheads being held in temporary aviaries 24 Appendix 3 Recipes for whitehead foods 25 Best practice techniques for the translocation of whiteheads (popokatea, Mohoua albicilla) Ralph Powlesland1 and Kevin Parker2 1 606 Manaroa Road, Manaroa, RD 2, Picton, New Zealand [email protected] 2 Parker Conservation, Auckland, New Zealand parkerconservation.co.nz Abstract This document outlines best practice techniques for the translocation of whiteheads (popokatea, Mohoua albicilla). -
Indonesia Schools' Booklet 2018
Indonesia Schools’ Booklet 2018 Contents 1. Study area and research objectives ...................................................................................... 2 2. Week 1 itinerary .................................................................................................................. 3 3. Jungle survival skills ........................................................................................................... 4 4. Week 1 lectures .................................................................................................................. 5 5. Biodiversity practicals ......................................................................................................... 6 6. Research contribution ......................................................................................................... 7 7. Week 2 itinerary .................................................................................................................. 8 8. Coral Reef Ecology Course .................................................................................................. 8 9. PADI Open Water Diver Course ............................................................................................ 9 10. PADI Open Water Referral Course .................................................................................... 10 11. Reef Ecology lectures and practicals ................................................................................ 12 12. A-Level exam board table ............................................................................................... -
Protected Area Management Plan Development - SAPO NATIONAL PARK
Technical Assistance Report Protected Area Management Plan Development - SAPO NATIONAL PARK - Sapo National Park -Vision Statement By the year 2010, a fully restored biodiversity, and well-maintained, properly managed Sapo National Park, with increased public understanding and acceptance, and improved quality of life in communities surrounding the Park. A Cooperative Accomplishment of USDA Forest Service, Forestry Development Authority and Conservation International Steve Anderson and Dennis Gordon- USDA Forest Service May 29, 2005 to June 17, 2005 - 1 - USDA Forest Service, Forestry Development Authority and Conservation International Protected Area Development Management Plan Development Technical Assistance Report Steve Anderson and Dennis Gordon 17 June 2005 Goal Provide support to the FDA, CI and FFI to review and update the Sapo NP management plan, establish a management plan template, develop a program of activities for implementing the plan, and train FDA staff in developing future management plans. Summary Week 1 – Arrived in Monrovia on 29 May and met with Forestry Development Authority (FDA) staff and our two counterpart hosts, Theo Freeman and Morris Kamara, heads of the Wildlife Conservation and Protected Area Management and Protected Area Management respectively. We decided to concentrate on the immediate implementation needs for Sapo NP rather than a revision of existing management plan. The four of us, along with Tyler Christie of Conservation International (CI), worked in the CI office on the following topics: FDA Immediate -
Supplementary Information For
Supplementary Information for Earth history and the passerine superradiation Oliveros, Carl H., Daniel J. Field, Daniel T. Ksepka, F. Keith Barker, Alexandre Aleixo, Michael J. Andersen, Per Alström, Brett W. Benz, Edward L. Braun, Michael J. Braun, Gustavo A. Bravo, Robb T. Brumfield, R. Terry Chesser, Santiago Claramunt, Joel Cracraft, Andrés M. Cuervo, Elizabeth P. Derryberry, Travis C. Glenn, Michael G. Harvey, Peter A. Hosner, Leo Joseph, Rebecca Kimball, Andrew L. Mack, Colin M. Miskelly, A. Townsend Peterson, Mark B. Robbins, Frederick H. Sheldon, Luís Fábio Silveira, Brian T. Smith, Noor D. White, Robert G. Moyle, Brant C. Faircloth Corresponding authors: Carl H. Oliveros, Email: [email protected] Brant C. Faircloth, Email: [email protected] This PDF file includes: Supplementary text Figs. S1 to S10 Table S1 to S3 References for SI reference citations Other supplementary materials for this manuscript include the following: Supplementary Files S1 to S3 1 www.pnas.org/cgi/doi/10.1073/pnas.1813206116 Supplementary Information Text Extended Materials and Methods Library preparation and sequencing. We extracted and purified DNA from fresh muscle tissue, liver tissue, or toepad clips from 113 vouchered museum specimens (Supplementary File S1) using the Qiagen DNeasy Blood and Tissue Kit following the manufacturer’s protocol. We quantified DNA extracts using a Qubit fluorometer, and we prepared aliquots of DNA extracted from muscle and liver at 10 ng/µL in 60 µL volume for shearing. We sheared each DNA sample to 400–600 bp using a Qsonica Q800R sonicator for 15–45 cycles, with each cycle running for 20 seconds on and 20 seconds off at 25% amplitude.