Notes on the Early Illustrations and the Juvenile Plumage Of
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Non-Native Trees Provide Habitat for Native Hawaiian Forest Birds
NON-NATIVE TREES PROVIDE HABITAT FOR NATIVE HAWAIIAN FOREST BIRDS By Peter J. Motyka A Thesis Submitted in Partial Fulfillment Of the Requirements for the Degree of Master of Science In Biology Northern Arizona University December 2016 Approved: Jeffrey T. Foster, Ph.D., Co-chair Tad C. Theimer, Ph. D., Co-chair Carol L. Chambers, Ph. D. ABSTRACT NON-NATIVE TREES PROVIDE HABITAT FOR NATIVE HAWAIIAN FOREST BIRDS PETER J. MOTYKA On the Hawaiian island of Maui, native forest birds occupy an area dominated by non- native plants that offers refuge from climate-limited diseases that threaten the birds’ persistence. This study documented the status of the bird populations and their ecology in this novel habitat. Using point-transect distance sampling, I surveyed for birds over five periods in 2013-2014 at 123 stations across the 20 km² Kula Forest Reserve (KFR). I documented abundance and densities for four native bird species: Maui ‘alauahio (Paroreomyza montana), ʻiʻiwi (Drepanis coccinea), ʻapapane (Himatione sanguinea), and Hawaiʻi ʻamakihi, (Chlorodrepanis virens), and three introduced bird species: Japanese white-eye (Zosterops japonicas), red-billed leiothrix (Leiothrix lutea), and house finch (Haemorhous mexicanus). I found that 1) native forest birds were as abundant as non-natives, 2) densities of native forest birds in the KFR were similar to those found in native forests, 3) native forest birds showed varying dependence on the structure of the habitats, with ʻiʻiwi and ‘alauahio densities 20 and 30 times greater in forest than in scrub, 4) Maui ‘alauahio foraged most often in non-native cape wattle, eucalyptus, and tropical ash, and nested most often in non-native Monterey cypress, Monterey pine, and eucalyptus. -
The Relationships of the Hawaiian Honeycreepers (Drepaninini) As Indicated by Dna-Dna Hybridization
THE RELATIONSHIPS OF THE HAWAIIAN HONEYCREEPERS (DREPANININI) AS INDICATED BY DNA-DNA HYBRIDIZATION CH^RrES G. SIBLEY AND Jo• E. AHLQUIST Departmentof Biologyand PeabodyMuseum of Natural History, Yale University, New Haven, Connecticut 06511 USA ABSTRACT.--Twenty-twospecies of Hawaiian honeycreepers(Fringillidae: Carduelinae: Drepaninini) are known. Their relationshipsto other groups of passefineswere examined by comparing the single-copyDNA sequencesof the Apapane (Himationesanguinea) with those of 5 speciesof carduelinefinches, 1 speciesof Fringilla, 15 speciesof New World nine- primaried oscines(Cardinalini, Emberizini, Thraupini, Parulini, Icterini), and members of 6 other families of oscines(Turdidae, Monarchidae, Dicaeidae, Sylviidae, Vireonidae, Cor- vidae). The DNA-DNA hybridization data support other evidence indicating that the Hawaiian honeycreepersshared a more recent common ancestorwith the cardue!ine finches than with any of the other groupsstudied and indicate that this divergenceoccurred in the mid-Miocene, 15-20 million yr ago. The colonizationof the Hawaiian Islandsby the ancestralspecies that radiated to produce the Hawaiian honeycreeperscould have occurredat any time between 20 and 5 million yr ago. Becausethe honeycreeperscaptured so many ecologicalniches, however, it seemslikely that their ancestor was the first passefine to become established in the islands and that it arrived there at the time of, or soon after, its separationfrom the carduelinelineage. If so, this colonist arrived before the present islands from Hawaii to French Frigate Shoal were formed by the volcanic"hot-spot" now under the island of Hawaii. Therefore,the ancestral drepaninine may have colonizedone or more of the older Hawaiian Islandsand/or Emperor Seamounts,which also were formed over the "hot-spot" and which reachedtheir present positions as the result of tectonic crustal movement. -
25 Using Community Group Monitoring Data to Measure The
25 Using Community Group Monitoring Data To Measure The Effectiveness Of Restoration Actions For Australia's Woodland Birds Michelle Gibson1, Jessica Walsh1,2, Nicki Taws5, Martine Maron1 1Centre for Biodiversity and Conservation Science, School of Earth and Environmental Sciences, University of Queensland, St Lucia, Brisbane, 4072, Queensland, Australia, 2School of Biological Sciences, Monash University, Clayton, Melbourne, 3800, Victoria, Australia, 3Greening Australia, Aranda, Canberra, 2614 Australian Capital Territory, Australia, 4BirdLife Australia, Carlton, Melbourne, 3053, Victoria, Australia, 5Greening Australia, PO Box 538 Jamison Centre, Macquarie, Australian Capital Territory 2614, Australia Before conservation actions are implemented, they should be evaluated for their effectiveness to ensure the best possible outcomes. However, many conservation actions are not implemented under an experimental framework, making it difficult to measure their effectiveness. Ecological monitoring datasets provide useful opportunities for measuring the effect of conservation actions and a baseline upon which adaptive management can be built. We measure the effect of conservation actions on Australian woodland ecosystems using two community group-led bird monitoring datasets. Australia’s temperate woodlands have been largely cleared for agricultural production and their bird communities are in decline. To reverse these declines, a suite of conservation actions has been implemented by government and non- government agencies, and private landholders. We analysed the response of total woodland bird abundance, species richness, and community condition, to two widely-used actions — grazing exclusion and replanting. We recorded 139 species from 134 sites and 1,389 surveys over a 20-year period. Grazing exclusion and replanting combined had strong positive effects on all three bird community metrics over time relative to control sites, where no actions had occurred. -
SAB 015 1994 P91-102 a Chronology of Ornithological
Studies in Avian Biology No. 15:91-102, 1994. A CHRONOLOGY OF ORNITHOLOGICAL EXPLORATION IN THE HAWAIIAN ISLANDS, FROM COOK TO PERKINS STORRS L. OLSON AND HELEN F. JAMES Abstract. Although ornithological exploration of the Hawaiian archipelago began in 1778, more than a century elapsed before reasonably comprehensive avifaunal surveys were conducted in the 1880s and 1890s. We review the history of early bird collecting for each of the major islands, based on examination of specimen data, archives, and the published literature. An island-by-island approach shows that some islands were more favored for visits by early collectors, while others, especially Maui, were long neglected. Given the uneven collecting histories of individual islands, we speculate that additional species and populations may have become extinct after first European contact, but before specimens were preserved for science. Key Words: Hawaiian Islands; history of ornithological collecting; historical extinctions; museum collections. Compared to many parts of the world, manner and timing of ornithological col- ornithological exploration got an early start lecting in the 19th century. Some species in the Hawaiian Islands, beginning with the and island populations of birds probably third and final voyage of Captain James survived undetected into the historic period Cook in 1778, which expedition marked the but were overtaken by extinction before first European contact with the islands. By specimens could be collected. To identify way of contrast, the first bird to be collected possible biases of this nature, it is instruc- for science in Panama, crossroads of world tive to examine the history of ornithological trade from the late 15th century onward, collecting on an island-by-island basis. -
Oct 1 4 2011
UNITED STATES CEPARTMENT OF COMMERCE National Oceanic and Atmospheric Administration NATIONAL MARINE FISHERIES SERVICE Silver Spring. MO 2081 0 OCT 1 4 2011 James A. Hanlon Director, EPA Office of Wastewater Management Room 7116A - EPA East 1201 Constitution Avenue, NW Washington, DC 20460 Mr. Hanlon: Enclosed is the National Marine Fisheries Service's (NMFS) Biological Opinion (Opinion), issued under the authority of section 7(a)(2) of the Endangered Species Act of 1973 (ESA) as amended, regarding the Environmental Protection Agency's (EPA's) proposal to issue a Pesticides General Permit (PGP). As proposed, the general permit will cover point source pesticide pollutant discharges to waters of the U.S. from pesticide applications in States and 1 Territories where the EPA is the permitting authority: Alaska , American Samoa, District of Columbia, Guam, Idaho, Johnston Atoll, Massachusetts, Midway Island, New Hampshire, New 1 Mexico, Northern Mariana Islands, Oklahoma , Puerto Rico, and Wake Island. The proposed pennit will also authorize pesticide pollutant discharges to waters of the U.S. resulting from pesticide applications on Federal lands in Colorado, Delaware, Vermont and Washington, as well as Indian lands nationwide. This Opinion is based on our review of the EPA's Biological Evaluation/or the Environmental Protection Agency's (EPA) Pesticides General Permit (PGP), reviews of the effectiveness of the National Pollution Discharge Elimination System (NPDES) program and compliance for existing general permits, pesticide risk assessments and Section 7(a)(2) consultations on pesticide uses, species status revie\vs, listing documents, recovery plans, reports on the status and trends of water quality, past and current research and population dynamics modeling, published and unpublished scientific information and other sources of information as discussed in greater detail in the Approach to the Assessment section of this draft Opinion. -
Hawaiian Birds 1972*
HAWAIIAN BIRDS 1972* ANDREW J. BERGER More kinds (species and subspecies) of birds have become extinct in Hawaii than on all continents’ of the world combined. These endemic Hawaiian birds have become ex- tinct since 1844l, and most of them have succumbed since the 1890s. Table 1 lists the endemic Hawaiian birds which are presumed to be extinct. Moreover, Hawaiian birds account for nearly one-half of the birds in the U. S. Bureau of Sport Fisheries and Wildlifes’ Red Book of rare and endangered species. The follow- ing list contains 16 of the rare and endangered Hawaiian birds: Newells’ Manx Shear- water (Puffinus puffinus newel&), Hawaiian Dark-rumped Petrel (Pterodroma phaeo- pygia sandwichensis), Harcourt s’ Storm Petrel (Oceanodroma Castro cryptoleucura), Nene or Hawaiian Goose (Branta sandvicensis), Koloa or Hawaiian Duck (Anas wyvilliana) , Laysan Duck (Anus laysanensis) , Hawaiian Hawk (Buteo solitarius) , Hawaiian Gallinule (Gallinula chloropus sandvicensis) , Hawaiian Coot (Fulica ameri- cana alai), Hawaiian Black-necked Stilt (Himantopus himantopus knudseni), Hawaiian Crow (Corvus tropicus), Large Kauai Thrush (Phaeornis obscurus myadestina), Molo- kai Thrush (Phaeornis o. rutha), Small Kauai Thrush (Phaeornis palmeri), Nihoa Millerbird (Acrocephalus familiaris kingi), and the Kauai 00 (Moho braccetus). TO this list may be added the non-migratory Hawaiian population of the Black-crowned Night Heron (Nycticorax n. hoactli). But, there are even more endangered Hawaiian birds! Because of their special interest to ornithologists, -
Abstracts of Those Ar- Dana L Moseley Ticles Using Packages Tm and Topicmodels in R to Ex- Graham E Derryberry Tract Common Words and Trends
ABSTRACT BOOK Listed alphabetically by last name of presenting author Oral Presentations . 2 Lightning Talks . 161 Posters . 166 AOS 2018 Meeting 9-14 April 2018 ORAL PRESENTATIONS Combining citizen science with targeted monitoring we argue how the framework allows for effective large- for Gulf of Mexico tidal marsh birds scale inference and integration of multiple monitoring efforts. Scientists and decision-makers are interested Evan M Adams in a range of outcomes at the regional scale, includ- Mark S Woodrey ing estimates of population size and population trend Scott A Rush to answering questions about how management actions Robert J Cooper or ecological questions influence bird populations. The SDM framework supports these inferences in several In 2010, the Deepwater Horizon oil spill affected many ways by: (1) monitoring projects with synergistic ac- marsh birds in the Gulf of Mexico; yet, a lack of prior tivities ranging from using approved standardized pro- monitoring data made assessing impacts to these the tocols, flexible data sharing policies, and leveraging population impacts difficult. As a result, the Gulf of multiple project partners; (2) rigorous data collection Mexico Avian Monitoring Network (GoMAMN) was that make it possible to integrate multiple monitoring established, with one of its objectives being to max- projects; and (3) monitoring efforts that cover multiple imize the value of avian monitoring projects across priorities such that projects designed for status assess- the region. However, large scale assessments of these ment can also be useful for learning or describing re- species are often limited, tidal marsh habitat in this re- sponses to management activities. -
Eulogies for Lost Species
Daniel Hudon Eulogies for Lost Species THE BUBAL HARTEBEEST Alcelaphus buselaphus buselaphus Though the Bubal Hartebeest carried its huge beam head as stylishly as possible, its melancholy eyes, humped shoul- ders, sloping quarters, and particularly its long, long face gave the antelope a deprecatory appearance, as if it were apologiz- ing for its very existence. Meekness was its virtue. Its small horns strikingly outlined the shape of a lyre though from the side their lazy curves made it seem like a pair of egrets had taken root and spent their time gazing hopelessly skyward. The Bubal Hartebeest moved at a smooth and swinging canter, flicking its rear legs fleetly as it ran with great endur- ance over the lowland mountains of Northern Africa. Chased, it easily fled its pursuers and, perhaps contrite, would often stop and stare its foe full in the face with a most humble look, as if it didn’t mean to escape, as if it couldn’t help itself. Then, with a violent sneeze, once more it would bolt ahead. THE BLACK MAMO Drepanis funerea Deep in the tubes of the lobelia flowers hid the nectar that was perpetually sought by the Black Mamo, a honeycreeper that was black from head to foot except for a small patch of yellow at the base of its absurdly long, curved bill. After for- aging from flower to flower, spending only a few seconds at CLARION 17 59 each, dipping in deep, rapidly darting their tongues in and out so they appeared like a liquid streak, their heads would emerge whimsically encrusted in pollen. -
Inferring Extinction in North American and Hawaiian Birds in the Presence of Sighting Uncertainty
Inferring extinction in North American and Hawaiian birds in the presence of sighting uncertainty David L. Roberts1 and Ivan Jari¢2,3 1 Durrell Institute of Conservation and Ecology, School of Anthropology & Conservation, University of Kent, Canterbury, Kent, United Kingdom 2 Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Berlin, Germany 3 Institute for Multidisciplinary Research, University of Belgrade, Belgrade, Serbia ABSTRACT For most species the timing of extinction events is uncertain, occurring sometime after the last sighting. However, the sightings themselves may also be uncertain. Recently a number of methods have been developed that incorporate sighting uncertainty in the inference of extinction based on a series of sightings. Here we estimate the timing of extinction for 41 of 52 North American and Hawaiian bird taxa and populations, the results of which suggest all became extinct before 2009. By acknowledging sighting uncertainty it results in two opposite effects, one pushing the timing of extinction away from the last sighting and the other drawing the timing of extinction nearer to it. However, for 14 assessed taxa and populations the upper 95% bounds lie beyond the end of the observation period and therefore suggest the possibility of continued persistence. This has important implications for conservation decision-makers and potentially reduces the likelihood of Romeo's Error. Subjects Biodiversity, Conservation Biology, Zoology Keywords Avian extinction, Conservation triage, Critically endangered, Sighting records, Sighting reliability, Species persistence Submitted 15 July 2016 Accepted 11 August 2016 INTRODUCTION Published 1 September 2016 For many species our knowledge of their persistence is based on sightings that vary in Corresponding author David L. -
A Systematic Analysis of the Endemic Avifauna of the Hawaiian Islands. Harold Douglas Pratt Rj Louisiana State University and Agricultural & Mechanical College
Louisiana State University LSU Digital Commons LSU Historical Dissertations and Theses Graduate School 1979 A Systematic Analysis of the Endemic Avifauna of the Hawaiian Islands. Harold Douglas Pratt rJ Louisiana State University and Agricultural & Mechanical College Follow this and additional works at: https://digitalcommons.lsu.edu/gradschool_disstheses Recommended Citation Pratt, Harold Douglas Jr, "A Systematic Analysis of the Endemic Avifauna of the Hawaiian Islands." (1979). LSU Historical Dissertations and Theses. 3347. https://digitalcommons.lsu.edu/gradschool_disstheses/3347 This Dissertation is brought to you for free and open access by the Graduate School at LSU Digital Commons. It has been accepted for inclusion in LSU Historical Dissertations and Theses by an authorized administrator of LSU Digital Commons. For more information, please contact [email protected]. INFORMATION TO USERS This was produced from a copy of a document sent to us for microfilming. While the most advanced technological means to photograph and reproduce this document have been used, the quality is heavily dependent upon the quality of the material submitted. The following explanation of techniques is provided to help you understand markings or notations which may appear on this reproduction. 1. The sign or “target” for pages apparently lacking from the document photographed is “Missing Page(s)”. If it was possible to obtain the missing page(s) or section, they are spliced into the film along with adjacent pages. This may have necessitated cutting through an image and duplicating adjacent pages to assure you of complete continuity. 2. When an image on the film is obliterated with a round black mark it is an indication that the Him inspector noticed either blurred copy because of movement during exposure, or duplicate copy. -
Iwi (Vestiaria Coccinea) As Threatened Or Endangered Under the U.S
PETITION TO LIST THE `I`IWI (VESTIARIA COCCINEA) AS THREATENED OR ENDANGERED UNDER THE U.S. ENDANGERED SPECIES ACT August 24, 2010 Center for Biological Diversity `I`IWI (VESTIARIA COCCINEA) Photo source: Wikipedia 1 August 24, 2010 Ken Salazar, Secretary of the Interior Robyn Thorson, Regional Director U.S. Department of the Interior U.S. Fish & Wildlife Service 1849 C Street N.W. Pacific Region Washington, DC 20240 911 NE 11th Ave Portland, Oregon 97232 Dear Secretary Salazar, The Center for Biological Diversity, Noah Greenwald, and Dr. Tony Povilitis formally petition to list the `I`iwi (Vestiaria coccinea) as a threatened or endangered species pursuant to the Endangered Species Act (ESA), 16 U.S.C. §1531 et seq. This petition is filed under 5 U.S.C. 553(e) and 50 CFR 424.14 (1990), which grant interested parties the right to petition for issuance of a rule from the Secretary of Interior. Under the ESA, a threatened species includes “any species which is likely to become an endangered species within the foreseeable future throughout all or a signification portion of its range.” An “endangered species” is one that is in danger of extinction. The `I`iwi warrants listing because it is imperiled by climate change and disease in combination with other factors, is declining in population size and range, and is not adequately protected by existing regulatory mechanisms. With climate change forcing the spread of avian malaria and avian pox, the `I`iwi is in danger of near term extinction in the western portion of its range (the islands of Kauai, Oahu, and Molokai, and on west Maui), and severe population declines with risk of extinction within the foreseeable future across its eastern range (east Maui and the island of Hawaii). -
Drepanidini Species Tree
Drepanidini: Hawaiian Honeycreepers Poo-uli, Melamprosops phaeosoma Akikiki / Kaui Creeper, Oreomystis bairdi ?Oahu Alauahio / Oahu Creeper, Paroreomyza maculata ?Kakawahie / Molokai Creeper, Paroreomyza flammea Maui Alauahio / Maui Creeper, Paroreomyza montana Laysan Finch, Telespiza cantans Nihoa Finch, Telespiza ultima Palila, Loxioides bailleui ?Kona Grosbeak, Chloridops kona ?Lesser Koa-Finch, Rhodacanthis flaviceps ?Greater Koa-Finch, Rhodacanthis palmeri ?Ula-ai-hawane, Ciridops anna Akohekohe / Crested Honeycreeper Drepanis dolei ?*Laysan Honeycreeper, Drepanis fraithii Apapane, Drepanis sanguinea Iiwi, Drepanis coccinea ?Black Mamo, Drepanis funerea ?Hawaii Mamo, Drepanis pacifica ?Greater Amakihi, Viridonia sagittirostris Anianiau, Magumma parva Hawaii Amakihi, Chlorodrepanis virens Kauai Amakihi, Chlorodrepanis stejnegeri Oahu Amakihi, Chlorodrepanis flavus Hawaii Creeper, Loxops mana Akekee / Kauai Akepa, Loxops caeruleirostris ?*Oahu Akepa, Loxops wolstenholmei ?*Maui Akepa, Loxops ochraceus Hawaii Akepa, Loxops coccineus ?Ou, Psittirostra psittacea ?Lanai Hookbill, Dysmorodrepanis munroi Maui Parrotbill / Kiwikiu, Pseudonestor xanthophrys ?Lesser Akialoa / Hawaii Akialoa, Hemignathus obscurus ?*Kauai Akialoa, Hemignathus stejnegeri ?Oahu Akialoa, Hemignathus ellisianus ?*Maui-nui Akialoa, Hemignathus lanaiensis Akiapolaau, Hemignathus wilsoni ?*Kauai Nukupuu, Hemignathus hanapepe ?Oahu Nukupuu, Hemignathus lucidus ?*Maui Nukupuu, Hemignathus affinis Notes: Stars denote recent splits. Red taxa are extinct, orange probably extinct. Question marks indicate that the species was not included in a genetic analysis. In that case the osteology-based phylogeny of James (2004) has generally been used to place the species on the tree. Sources: James (2004), Knowlton et al. (2014), Lerner et al. (2011). Older versions also used Arnaiz-Villena et al. (2007b), Fleischer et al. (2001), Pratt (2001), Reding et al. (2009)..