Non-Native Trees Provide Habitat for Native Hawaiian Forest Birds
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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. -
Department of the Interior Fish and Wildlife Service
Thursday, February 27, 2003 Part II Department of the Interior Fish and Wildlife Service 50 CFR Part 17 Endangered and Threatened Wildlife and Plants; Final Designation or Nondesignation of Critical Habitat for 95 Plant Species From the Islands of Kauai and Niihau, HI; Final Rule VerDate Jan<31>2003 13:12 Feb 26, 2003 Jkt 200001 PO 00000 Frm 00001 Fmt 4717 Sfmt 4717 E:\FR\FM\27FER2.SGM 27FER2 9116 Federal Register / Vol. 68, No. 39 / Thursday, February 27, 2003 / Rules and Regulations DEPARTMENT OF THE INTERIOR units designated for the 83 species. This FOR FURTHER INFORMATION CONTACT: Paul critical habitat designation requires the Henson, Field Supervisor, Pacific Fish and Wildlife Service Service to consult under section 7 of the Islands Office at the above address Act with regard to actions carried out, (telephone 808/541–3441; facsimile 50 CFR Part 17 funded, or authorized by a Federal 808/541–3470). agency. Section 4 of the Act requires us SUPPLEMENTARY INFORMATION: RIN 1018–AG71 to consider economic and other relevant impacts when specifying any particular Background Endangered and Threatened Wildlife area as critical habitat. This rule also and Plants; Final Designation or In the Lists of Endangered and determines that designating critical Nondesignation of Critical Habitat for Threatened Plants (50 CFR 17.12), there habitat would not be prudent for seven 95 Plant Species From the Islands of are 95 plant species that, at the time of species. We solicited data and Kauai and Niihau, HI listing, were reported from the islands comments from the public on all aspects of Kauai and/or Niihau (Table 1). -
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 ................................................................................................................................ -
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~. -
Guideline 410 Prohibited Plant List
VENTURA COUNTY FIRE PROTECTION DISTRICT FIRE PREVENTION BUREAU 165 DURLEY AVENUE CAMARILLO, CA 93010 www.vcfd.org Office: 805-389-9738 Fax: 805-388-4356 GUIDELINE 410 PROHIBITED PLANT LIST This list was first published by the VCFD in 2014. It has been updated as of April 2019. It is intended to provide a list of plants and trees that are not allowed within a new required defensible space (DS) or fuel modification zone (FMZ). It is highly recommended that these plants and trees be thinned and or removed from existing DS and FMZs. In certain instances, the Fire Department may require the thinning and or removal. This list was prepared by Hunt Research Corporation and Dudek & Associates, and reviewed by Scott Franklin Consulting Co, VCFD has added some plants and has removed plants only listed due to freezing hazard. Please see notes after the list of plants. For questions regarding this list, please contact the Fire Hazard reduction Program (FHRP) Unit at 085-389-9759 or [email protected] Prohibited plant list:Botanical Name Common Name Comment* Trees Abies species Fir F Acacia species (numerous) Acacia F, I Agonis juniperina Juniper Myrtle F Araucaria species (A. heterophylla, A. Araucaria (Norfolk Island Pine, Monkey F araucana, A. bidwillii) Puzzle Tree, Bunya Bunya) Callistemon species (C. citrinus, C. rosea, C. Bottlebrush (Lemon, Rose, Weeping) F viminalis) Calocedrus decurrens Incense Cedar F Casuarina cunninghamiana River She-Oak F Cedrus species (C. atlantica, C. deodara) Cedar (Atlas, Deodar) F Chamaecyparis species (numerous) False Cypress F Cinnamomum camphora Camphor F Cryptomeria japonica Japanese Cryptomeria F Cupressocyparis leylandii Leyland Cypress F Cupressus species (C. -
Ecophysiology and Reproductive Biology of Cultivated Cacti
04 Ecophysiology and reproductive biology of cultivated cacti Paolo Inglesea,Giorgia Liguoria and Erick de la Barrerab a Department of Agricultural and Forestry Sciences, University of Palermo, Italy b Institute of Research in Ecosystems, National Autonomous University of Mexico, Mexico City, Mexico Ecophysiology and reproductive biology 04 of cultivated cacti INTRODUCTION Mojave Desert in California, or the Rajasthan Desert in India (Felker and Inglese, 2003). Le Houérou (2002) de- Cactus pear − Opuntia fcus-indica (L.) Mill. − is a CAM scribes plantations in Aziza (Lybia) where the maximum (crassulacean acid metabolism) plant cultivated in a wide temperature may exceed 50° C. O. fcus-indica cladode range of environments, resulting in major differences in cannot survive at 70° C (Nobel, 2002). plant survival and development, and in crop potential. The fruits of O. fcus-indica can be harvested from July The ecological success of opuntias, specifcally O. f- to November in the Northern Hemisphere − Mediterra- cus-indica, is due largely to their peculiar daily pattern nean Basin, California, and Mexico − and from January of carbon uptake and water loss, both of which occur to April in the Southern Hemisphere, depending on mostly at night. Like other CAM plants, cactus pear the genotype and genotype × environment interac- opens its stomata at night to fx CO2 and accumulate tion. Natural or induced refowering may extend the and store malate in the vacuoles of the chlorenchyma ripening period to January-February in the Northern cells. Since night-time temperatures are lower than di- Hemisphere and to September-October in the South- urnal ones, and relative humidity is generally higher, the ern Hemisphere. -
List 01 Hawaiian Names 01 Plants
V\.{). 3 v BOTANICAL BULLETIN NO.2 JUNE. 1913 TERRITORY OF HAWAII BOARD OF AGRICULTURE AND FORESTRY List 01 Hawaiian Names 01 Plants BY JOSEPH F. ROCK Consulting Botanist, Board of Agriculture and Forestry HONOLULU: HAWAIIAN GAZETTE CO., LTD. 1913 ALPHABETICAL LIST OF HAWAIIAN NAMES OF PLANTS. The following list of Hawaiian plant-names has been compiled from various sources. Hillebrand in his valuable Flora of the Hawaiian Islands has given many Hawaiian names, especially of the more common species; these are incorporated in this list with a few corrections. Nearly all Hawaiian plant-names found in this list and not in Hillebrand's Flora were secured from Mr. Francis Gay of the Island of Kauai, an old resident in this Terri tory and well acquainted with its plants from a layman's stand point. It was the writer's privilege to camp with Mr. Gay in the mountains of Kauai collecting botanical material; for almost every species he could give the native name, which he had se cured in the early days from old and reliable natives. Mr. Gay had made spatter prints of many of the native plants in a large record book with their names and uses, as well as their symbolic meaning when occurring in mele (songs) or olioli (chants), at tached to them. For all this information the writer is indebted mainly to Mr. Francis Gay and also to Mr. Augustus F. Knudsen of the same Island. The writer also secured Hawaiian names from old na tives and Kahunas (priests) in the various islands of the group. -
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. -
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.