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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 ................................................................................................................................ -
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~. -
Pacific Islands Area
Habitat Planting for Pollinators Pacific Islands Area November 2014 The Xerces Society for Invertebrate Conservation www.xerces.org Acknowledgements This document is the result of collaboration with state and federal agencies and educational institutions. The authors would like to express their sincere gratitude for the technical assistance and time spent suggesting, advising, reviewing, and editing. In particular, we would like to thank the staff at the Hoolehua Plant Materials Center on the Hawaiian Island of Molokai, NRCS staff in Hawaii and American Samoa, and researchers and extension personnel at American Samoa Community College Land Grant (especially Mark Schmaedick). Authors Written by Jolie Goldenetz-Dollar (American Samoa Community College), Brianna Borders, Eric Lee- Mäder, and Mace Vaughan (The Xerces Society for Invertebrate Conservation), and Gregory Koob, Kawika Duvauchelle, and Glenn Sakamoto (USDA Natural Resources Conservation Service). Editing and layout Ashley Minnerath (The Xerces Society). Updated November 2014 by Sara Morris, Emily Krafft, and Anne Stine (The Xerces Society). Photographs We thank the photographers who generously allowed use of their images. Copyright of all photographs remains with the photographers. Cover main: Jolie Goldenetz-Dollar, American Samoa Community College. Cover bottom left: John Kaia, Lahaina Photography. Cover bottom right: Gregory Koob, Hawaii Natural Resources Conservation Service. Funding This technical note was funded by the U.S. Department of Agriculture (USDA) Natural Resources Conservation Service (NRCS) and produced jointly by the NRCS and The Xerces Society for Invertebrate Conservation. Additional support was provided by the National Institute for Food and Agriculture (USDA). Please contact Tony Ingersoll ([email protected]) for more information about this publication. -
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. -
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. -
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. -
Akeake (Dodonaea Viscosa) Number 26
Akeake (Dodonaea viscosa) Number 26 DESCRIPTION Akeake is easily recognised by its distinctive bright green long thin wavy leaves, flaking bark and its papery winged seed capsules. It is a hardy, coastal shrub or small tree. In the right conditions, it will grow to about 10m high with a spreading crown and a trunk of around 30cm in diameter. The leaves are alternate, thin, light green with smooth margins and raised veins. The bark is reddish brown and peels off in long, thin strips. Akeake flowers are non-descript. They form in panicles at the end of branches from spring through to mid-summer. The fruit, however, are very visible as a capsule with two to four pale yellow wings which turn brown when dry and ripe. There are usually one or two seeds per capsule. DISTRIBUTION Akeake is native to New Zealand and grows throughout the North Island and northern parts of the South Island. It has also been found on the Chatham Islands, where it may have been introduced. It is also widely distributed through the Southern Hemisphere, with different subspecies and varieties in Australia, Southeast Asia, Africa and Latin CONSERVATION America. Akeake is not a nationally threatened or endangered plant. It is recognised as being Akeake naturally occurs in coastal and regionally distinctive, as it is generally lowland zones, favouring areas of open uncommon in the Taranaki region. forest or scrub. It prefers drier sites such as coastal river valleys, steep hillsides and THREATS cliffs and stabilised dunes. It is drought- Trampling and browsing by domestic tolerant and will handle light frosts. -
Apapane (Himatione Sanguinea)
The Birds of North America, No. 296, 1997 STEVEN G. FANCY AND C. JOHN RALPH 'Apapane Himatione sanguinea he 'Apapane is the most abundant species of Hawaiian honeycreeper and is perhaps best known for its wide- ranging flights in search of localized blooms of ō'hi'a (Metrosideros polymorpha) flowers, its primary food source. 'Apapane are common in mesic and wet forests above 1,000 m elevation on the islands of Hawai'i, Maui, and Kaua'i; locally common at higher elevations on O'ahu; and rare or absent on Lāna'i and Moloka'i. density may exceed 3,000 birds/km2 The 'Apapane and the 'I'iwi (Vestiaria at times of 'ōhi'a flowering, among coccinea) are the only two species of Hawaiian the highest for a noncolonial honeycreeper in which the same subspecies species. Birds in breeding condition occurs on more than one island, although may be found in any month of the historically this is also true of the now very rare year, but peak breeding occurs 'Ō'ū (Psittirostra psittacea). The highest densities February through June. Pairs of 'Apapane are found in forests dominated by remain together during the breeding 'ōhi'a and above the distribution of mosquitoes, season and defend a small area which transmit avian malaria and avian pox to around the nest, but most 'Apapane native birds. The widespread movements of the 'Apapane in response to the seasonal and patchy distribution of ' ōhi'a The flowering have important implications for disease Birds of transmission, since the North 'Apapane is a primary carrier of avian malaria and America avian pox in Hawai'i.