Apapane (Himatione Sanguinea)
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Saint Louis Encephalitis (SLE)
Encephalitis, SLE Annual Report 2018 Saint Louis Encephalitis (SLE) Saint Louis Encephalitis is a Class B Disease and must be reported to the state within one business day. St. Louis Encephalitis (SLE), a flavivirus, was first recognized in 1933 in St. Louis, Missouri during an outbreak of over 1,000 cases. Less than 1% of infections manifest as clinically apparent disease cases. From 2007 to 2016, an average of seven disease cases were reported annually in the United States. SLE cases occur in unpredictable, intermittent outbreaks or sporadic cases during the late summer and fall. The incubation period for SLE is five to 15 days. The illness is usually benign, consisting of fever and headache; most ill persons recover completely. Severe disease is occasionally seen in young children but is more common in adults older than 40 years of age, with almost 90% of elderly persons with SLE disease developing encephalitis. Five to 15% of cases die from complications of this disease; the risk of fatality increases with age in older adults. Arboviral encephalitis can be prevented by taking personal protection measures such as: a) Applying mosquito repellent to exposed skin b) Wearing protective clothing such as light colored, loose fitting, long sleeved shirts and pants c) Eliminating mosquito breeding sites near residences by emptying containers which hold stagnant water d) Using fine mesh screens on doors and windows. In the 1960s, there were 27 sporadic cases; in the 1970s, there were 20. In 1980, there was an outbreak of 12 cases in New Orleans. In the 1990s, there were seven sporadic cases and two outbreaks; one outbreak in 1994 in New Orleans (16 cases), and the other in 1998 in Jefferson Parish (14 cases). -
Convergent Evolution of 'Creepers' in the Hawaiian Honeycreeper
ARTICLE IN PRESS Biol. Lett. 1. INTRODUCTION doi:10.1098/rsbl.2008.0589 Adaptive radiation is a fascinating evolutionary pro- 1 cess that has generated much biodiversity. Although 65 2 Evolutionary biology several mechanisms may be responsible for such 66 3 diversification, the ‘ecological theory’ holds that it is 67 4 the outcome of divergent natural selection between 68 5 Convergent evolution of environments (Schluter 2000). Whether adaptive 69 6 radiations result chiefly from such ecological speciation, 70 7 ‘creepers’ in the Hawaiian however, remains unclear (Schluter 2001). Convergent 71 8 evolution is often considered powerful evidence for the 72 9 honeycreeper radiation role of adaptive forces in the speciation process 73 (Futuyma 1998), and thus documenting cases where it 10 Dawn M. Reding1,2,*, Jeffrey T. Foster1,3, 74 has occurred is important in understanding the link 11 Helen F. James4, H. Douglas Pratt5 75 12 between natural selection and adaptive radiation. 76 and Robert C. Fleischer1 13 The more than 50 species of Hawaiian honeycree- 77 1 14 Center for Conservation and Evolutionary Genetics, National pers (subfamily Drepanidinae) are a spectacular 78 Zoological Park and National Museum of Natural History, 15 Smithsonian Institution, Washington, DC 20008, USA example of adaptive radiation and an interesting 79 16 2Department of Zoology, University of Hawaii, Honolulu, system to test for convergence, which has been 80 17 HI 96822, USA suspected among the nuthatch-like ‘creeper’ eco- 81 3Center for Microbial Genetics & Genomics, -
Aspects of House Finch Breeding Biology in Hawaii
ASPECTS OF HOUSE FINCH BREEDING BIOLOGY IN HAWAII CHARLES VAN RIPER III Bent (1968) summarized information avail- Puu Laau, is the last remaining major mamane-naio able on the breeding biology of the House forest in Hawaii. Finch ( Curpodacus mexicanus). Although The stippled areas of figure 1 represent a broad spectrum of the forest types on the island of Hawaii; this species has been studied quite extensively included are native, introduced, and mixed stands of in its North American home range, little atten- vegetation. Areas 2, 3, and 5 are dry forest regions tion has been paid to it in Hawaii. Grinnell with annual rainfall of 76 cm or less; Puu Laau (2) (1911) reported on different color patterns of has mean annual rainfall of 50 cm, Puu Waawaa (3) 64 cm, and Puu Lehua (5) has 76 cm. The Kohala the House Finch in Hawaii, and Richardson Mountain complex ( 1) has a mean annual rainfall of and Bowles (1964) mentioned that on 23 June 229 cm, Puu 00 (4) has 483 cm, and the Kulani- 1960 they found a nestling that had fallen from Mauna Loa complex (6) has 317 cm. its nest on Kauai. On Mauna Kea, Berger Birds were mist-netted, color-banded, and released (1972) found House Finch nests with eggs from 1971 through 1973. Nest and tree heights were taken with a clinometer when it was impractical to as early as 6 April (1968) and as late as 17 use a tape measure. Nests and eggs were measured July (1967). Eleven nests were built on hori- with calipers and weighed on a sensitive spring bal- zontal branches of mamane (Sophora chryso- ance. -
Downloadable Data Collection
Smetzer et al. Movement Ecology (2021) 9:36 https://doi.org/10.1186/s40462-021-00275-5 RESEARCH Open Access Individual and seasonal variation in the movement behavior of two tropical nectarivorous birds Jennifer R. Smetzer1* , Kristina L. Paxton1 and Eben H. Paxton2 Abstract Background: Movement of animals directly affects individual fitness, yet fine spatial and temporal resolution movement behavior has been studied in relatively few small species, particularly in the tropics. Nectarivorous Hawaiian honeycreepers are believed to be highly mobile throughout the year, but their fine-scale movement patterns remain unknown. The movement behavior of these crucial pollinators has important implications for forest ecology, and for mortality from avian malaria (Plasmodium relictum), an introduced disease that does not occur in high-elevation forests where Hawaiian honeycreepers primarily breed. Methods: We used an automated radio telemetry network to track the movement of two Hawaiian honeycreeper species, the ʻapapane (Himatione sanguinea) and ʻiʻiwi (Drepanis coccinea). We collected high temporal and spatial resolution data across the annual cycle. We identified movement strategies using a multivariate analysis of movement metrics and assessed seasonal changes in movement behavior. Results: Both species exhibited multiple movement strategies including sedentary, central place foraging, commuting, and nomadism , and these movement strategies occurred simultaneously across the population. We observed a high degree of intraspecific variability at the individual and population level. The timing of the movement strategies corresponded well with regional bloom patterns of ‘ōhi‘a(Metrosideros polymorpha) the primary nectar source for the focal species. Birds made long-distance flights, including multi-day forays outside the tracking array, but exhibited a high degree of fidelity to a core use area, even in the non-breeding period. -
Keauhou Bird Conservation Center
KEAUHOU BIRD CONSERVATION CENTER Discovery Forest Restoration Project PO Box 2037 Kamuela, HI 96743 Tel +1 808 776 9900 Fax +1 808 776 9901 Responsible Forester: Nicholas Koch [email protected] +1 808 319 2372 (direct) Table of Contents 1. CLIENT AND PROPERTY INFORMATION .................................................................... 4 1.1. Client ................................................................................................................................................ 4 1.2. Consultant ....................................................................................................................................... 4 2. Executive Summary .................................................................................................. 5 3. Introduction ............................................................................................................. 6 3.1. Site description ............................................................................................................................... 6 3.1.1. Parcel and location .................................................................................................................. 6 3.1.2. Site History ................................................................................................................................ 6 3.2. Plant ecosystems ............................................................................................................................ 6 3.2.1. Hydrology ................................................................................................................................ -
Dacninae Species Tree, Part I
Dacninae I: Nemosiini, Conirostrini, & Diglossini Hooded Tanager, Nemosia pileata Cherry-throated Tanager, Nemosia rourei Nemosiini Blue-backed Tanager, Cyanicterus cyanicterus White-capped Tanager, Sericossypha albocristata Scarlet-throated Tanager, Sericossypha loricata Bicolored Conebill, Conirostrum bicolor Pearly-breasted Conebill, Conirostrum margaritae Chestnut-vented Conebill, Conirostrum speciosum Conirostrini White-eared Conebill, Conirostrum leucogenys Capped Conebill, Conirostrum albifrons Giant Conebill, Conirostrum binghami Blue-backed Conebill, Conirostrum sitticolor White-browed Conebill, Conirostrum ferrugineiventre Tamarugo Conebill, Conirostrum tamarugense Rufous-browed Conebill, Conirostrum rufum Cinereous Conebill, Conirostrum cinereum Stripe-tailed Yellow-Finch, Pseudochloris citrina Gray-hooded Sierra Finch, Phrygilus gayi Patagonian Sierra Finch, Phrygilus patagonicus Peruvian Sierra Finch, Phrygilus punensis Black-hooded Sierra Finch, Phrygilus atriceps Gough Finch, Rowettia goughensis White-bridled Finch, Melanodera melanodera Yellow-bridled Finch, Melanodera xanthogramma Inaccessible Island Finch, Nesospiza acunhae Nightingale Island Finch, Nesospiza questi Wilkins’s Finch, Nesospiza wilkinsi Saffron Finch, Sicalis flaveola Grassland Yellow-Finch, Sicalis luteola Orange-fronted Yellow-Finch, Sicalis columbiana Sulphur-throated Finch, Sicalis taczanowskii Bright-rumped Yellow-Finch, Sicalis uropigyalis Citron-headed Yellow-Finch, Sicalis luteocephala Patagonian Yellow-Finch, Sicalis lebruni Greenish Yellow-Finch, -
Synonymies for Indigenous Hawaiian Bird Taxa
Part 2 - Drepaninines Click here for Part 1 - Non-Drepaninines The Birds of the Hawaiian Islands: Occurrence, History, Distribution, and Status Version 2 - 1 January 2017 Robert L. Pyle and Peter Pyle Synonymies for Indigenous Hawaiian Bird Taxa Intensive ornithological surveying by active collectors during the latter 1890s led to several classic publications at the turn of the century, each covering nearly all species and island forms of native Hawaiian birds (Wilson and Evans 1899, Rothschild (1900),schild 1900, Bryan 1901a, Henshaw (1902a), 1902a, Perkins (1903),1903). The related but diverse scientific names appearing in these publications comprised the basis for scientific nomenclature for the next half century, but in many cases were modified by later authors using modern techniques to reach a current nomenclature provided in the American Ornithologists’ Union (AOU) Check-List, and followed (for the most part) at this site. A few current AOU names are still controversial, and more changes will come in the future. Synonymies reflecting the history of taxonomic nomenclature are listed below for all endemic birds in the Hawaiian Islands. The heading for each taxon represents that used in this book, reflecting the name used by the AOU (1998), as changed in subsequent AOU Supplements, or, in a few cases, as modified here based on more recent work or on differing opinions on taxonomic ranking. Previously recognized names are listed and citations included for classic publications on taxonomy of Hawaiian birds, as well as significant papers that influenced the species nomenclature. We thank Storrs Olson for sharing with us his summarization on the taxonomy and naming of indigenous Hawaiian birds. -
Twenty-Three of 69 Since Discovery of 17 SOME LIMITING
17 SOME LIMITING FACTORS AND RESEARCH NEEDS OF ENDANGERED HAWAIIAN FOREST BIRDS Winston E. Banko U. S. Fish & Wildlife Service Hawaii Volcanoes National Park Hawaii 96718 It is well known that Hawaiian birds are particularly sus ceptible to depopulation and extinction. Twenty-three of 69 endemic species or races have disappeared since discovery of Hawai'i by Europeans 200 years ago. Except for Warner (1968) and Atkinson (1977), only super ficial inquiries have been made into historical aspects and underlying factors of the Hawaiian forest bird decline. After several years of field and laboratory investigation, Warner explained th~ rlisappearance of forest birds as being caused primarily by disease. Atkinson advanced a theory based on historical evidence that arboreal predation by rats was a leading factor. The object of my long-term historical investigation is to document and compare the salient facts on the geography and chro nology of Hawaiian bird loss, species by species; to chronicle what is known about all factors of depopulation~-predation, disease, habitat alteration, and food competition; and to draw such conclusions as seem warranted. At the First Conference in Natural Sciences two years ago, Banko and Banko (1976) reported on the potential significance of food depletion in the decline of Hawaiian forest birds. The role played by the Big-headed ant (Pheidole megacephala) in destroying much of the endemic insect fauna at elevations generally less than 3000 feet (914 m) before 1890 was sketched at that time. (The term "insect" will be used hereafter as including other arthropods as well). I now wish to elaborate on the possible impact of foreign parasitic flies and .wasps in depleting native insect foods impor tant to the small Hawaiian forest birds at higher elevation~. -
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. -
2019 Kiwikiu Conservation Translocation Report
2019 Kiwikiu Conservation Translocation Report Christopher C. Warren1, Laura K. Berthold1, Hanna L. Mounce1, Peter Luscomb2, Bryce Masuda3, Lainie Berry4 2020 Maui Forest Bird Recovery Project1 Pacific Bird Conservation2 San Diego Zoo Global3 State of Hawaiʻi, Department of Land and Natural Resources, Division of Forestry and Wildlife4 Suggested citation – Warren, C.C., L.K. Berthold, H.L. Mounce, P. Luscomb, B. Masuda. L. Berry. 2020. Kiwikiu Translocation Report 2019. Internal Report. Pages 1–101. Cover photo by Bret Mossman. Translocated female, WILD11, in Kahikinui Hawaiian Homelands. Photo credits – Photographs were supplied by Maui Forest Bird Recovery Project (MFBRP) staff, members of the press, and volunteers. Photographer credit is given for those not taken by MFBRP staff. The 2019 kiwikiu translocation was a joint operation conducted by member organizations of the Maui Forest Bird Working Group. Organizations that conducted the translocation included American Bird Conservancy, Maui Forest Bird Recovery Project, National Park Service, Pacific Bird Conservation, San Diego Zoo Global, State of Hawaiʻi Department of Land and Natural Resources – Division of Forestry and Wildlife, The Nature Conservancy of Hawai‘i, U.S. Fish & Wildlife Service, and U.S. Geological Survey. In addition to representatives of these organizations, six community volunteers aided in these efforts. This does not include the dozens of volunteers and other organizations involved in planning for the translocation and preparing the release site through restoration and other activities. These efforts were greatly supported by the skilled pilots at Windward Aviation. i Table of Contents 1. Summary of 2019 Reintroduction ......................................................................................................... 1 2. Background of the Reintroduction ....................................................................................................... 1 2.1. -
Potentialities for Accidental Establishment of Exotic Mosquitoes in Hawaii1
Vol. XVII, No. 3, August, 1961 403 Potentialities for Accidental Establishment of Exotic Mosquitoes in Hawaii1 C. R. Joyce PUBLIC HEALTH SERVICE QUARANTINE STATION U.S. DEPARTMENT OF HEALTH, EDUCATION, AND WELFARE HONOLULU, HAWAII Public health workers frequently become concerned over the possibility of the introduction of exotic anophelines or other mosquito disease vectors into Hawaii. It is well known that many species of insects have been dispersed by various means of transportation and have become established along world trade routes. Hawaii is very fortunate in having so few species of disease-carrying or pest mosquitoes. Actually only three species are found here, exclusive of the two purposely introduced Toxorhynchites. Mosquitoes still get aboard aircraft and surface vessels, however, and some have been transported to new areas where they have become established (Hughes and Porter, 1956). Mosquitoes were unknown in Hawaii until early in the 19th century (Hardy, I960). The night biting mosquito, Culex quinquefasciatus Say, is believed to have arrived by sailing vessels between 1826 and 1830, breeding in water casks aboard the vessels. Van Dine (1904) indicated that mosquitoes were introduced into the port of Lahaina, Maui, in 1826 by the "Wellington." The early sailing vessels are known to have been commonly plagued with mosquitoes breeding in their water supply, in wooden tanks, barrels, lifeboats, and other fresh water con tainers aboard the vessels, The two day biting mosquitoes, Aedes ae^pti (Linnaeus) and Aedes albopictus (Skuse) arrived somewhat later, presumably on sailing vessels. Aedes aegypti probably came from the east and Aedes albopictus came from the western Pacific.