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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. -
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 ................................................................................................................................ -
Restoring the Wiliwili Forest of Waikoloa by Jen Lawson, Waikoloa Dry Forest Initiative
Restoring the Wiliwili Forest of Waikoloa by Jen Lawson, Waikoloa Dry Forest Initiative Waikoloa Village on Hawai‘i Island was built in an area that was once a native Ha- waiian tropical dryland forest, one of the most biologically diverse and beautiful eco- systems of our islands. Not that a casual ob- server would know that looking at Waikoloa today. The lowland dry forests of the past have been almost completely lost, largely due to human activities, the introduction and ex- pansion of feral ungulates, invasive plant spe- cies and an increase in fire frequency. What is left is precious. Although fragmented and degraded, the areas of native forest that still persist are precious, beautiful and inspiring Wiliwili flower places and the wiliwili forest of Waikoloa is one of those amazing places worthy of preservation. In 2003 members of the Waikoloa Village community, that would later form the Waikoloa Dry For- est Initiative (WDFI), saw something startling happening in their community. Ancient wiliwili (Erythrina sandwicensis) trees were being removed from the native soil that had been their home for hundreds of years and being transplanted into the landscapes of wiliwili enthusiasts wealthy enough to procure one from the wild. The small group of citizen stewards was effective in preventing the removal and sale of any more wiliwili trees in the area and also began a movement to change the future of the landscape in Waikoloa. Today WDFI manages the Waikoloa Dry Forest Preserve which protects nearly 300 acres of lowland dry forest including many of the wiliwili trees that remain in the area. -
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~. -
Pua Ka Wiliwili, Nanahu Ka Manō: Understanding Sharks in Pua Ka
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Digital Commons@Wayne State University Wayne State University Human Biology Open Access Pre-Prints WSU Press 7-1-2020 Pua ka Wiliwili, Nanahu ka Manō: Understanding Sharks in Hawaiian Culture Noelani Puniwai University of Hawaiʻi at Mānoa Follow this and additional works at: https://digitalcommons.wayne.edu/humbiol_preprints Recommended Citation Puniwai, Noelani, "Pua ka Wiliwili, Nanahu ka Manō: Understanding Sharks in Hawaiian Culture" (2020). Human Biology Open Access Pre-Prints. 174. https://digitalcommons.wayne.edu/humbiol_preprints/174 This Article is brought to you for free and open access by the WSU Press at DigitalCommons@WayneState. It has been accepted for inclusion in Human Biology Open Access Pre-Prints by an authorized administrator of DigitalCommons@WayneState. Pua ka Wiliwili, Nanahu ka Manō: Understanding Sharks in Hawaiian Culture Noelani Puniwai1* 1Kamakakūokalani Center for Hawaiian Studies, University of Hawaiʻi at Mānoa, Honolulu, Hawaiʻi, USA. *Correspondence to: Noelani Puniwai, Kamakakūokalani Center for Hawaiian Studies, University of Hawaiʻi at Mānoa, 2645 Dole Street, Room 209BB, Honolulu, HI 96822 USA. E- mail: [email protected]. Short Title: Understanding Sharks in Hawaiian Culture KEY WORDS: SHARKS, WORLDVIEW, CLASSIFICATION, HAWAI’I, LANGUAGE. Abstract Kanaka maoli (Indigenous Hawaiians) are blessed with a written literature that documents observations and relationships with our environment in the form of chants, stories, and genealogies passed down orally for centuries. These literatures connect us to our ancestral knowledge and highlight species, places, and processes of importance. Sayings, such as this one from the Kumulipo (our creation story) Pua ka wiliwili, nanahu ka manō, is an example of the place of nature, man, and a specific creature the shark in ecological phenology. -
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. -
Wiliwili Gall Wasp Invasion Length: One Class Period with Optional Homework Assignment
Activity #6 Invasive Species Unit 3 Activity #6 Wiliwili Gall Wasp Invasion Length: One class period with optional homework assignment Prerequisite Activity: None Objectives: • Trace the path of the 2005 wiliwili gall wasp invasion on Maui using real-life data. • Identify vectors ad pathways that facilitate the spread of invasive species. • Devise strategies for stopping an invasive pest. • Predict the efficacy of control strategies, based on existing and plausible environmental factors. Vocabulary: biological control (or biocontrol) Erythrina gall wasp (EGW) deciduous vector dormancy ••• Class Period One: Exploring the Gall Wasp Invasion on Google Earth In Advance This exercise requires access to Google Earth (free software available for download at www.earth. google.com) and the Wiliwili Gall Wasp Hoike.kmz file (included with this curriculum and available for download at www.hoikecurriculum.org). It’s best to pre-load computers with the program and file, rather than use class time to do so. Ideally students will work in small groups at their own computers as you lead them through the lesson, using a projector and screen. If that’s not possible, a single computer and projector will suffice. Prior to teaching the lesson, open Google Earth. If you’re using the software for the first time, take a few moments to learn how zoom, pan, search, etc. using the “Navigating Google Earth” tutorial avail- able at www.earth.google.com. It is best, though not necessary, to use Google Earth while connected to the Internet. Explore the Wiliwili Gall -
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. -
Remnant Wiliwili Forest Habitat at Wailea 670, Maui, Hawai`I: II. Comments on the Draft Environmental Impact Statement
SPECIAL REPORT Maui Ecosystems at Risk Remnant Wiliwili Forest Habitat at Wailea 670, Maui, Hawai`i: II. Comments On the Draft Environmental Impact Statement AUGUST 2010 Lee Altenberg, Ph.D. Associate Editor, BioSystems Journal (Elsevier) Kihei, Maui, Hawai`i 96753-7118 • telephone: 808.875.0745 • [email protected] • dynamics.org/Wailea670 Wiliwili Forest at Wailea 670: II. Comments on Draft EIS!Lee Altenberg Summary The proposed project represents the largest deliberate destruction of lowland Ha- waiian dry forest ecosystem to occur on Maui in decades. Lowland Hawaiian dry forest ecosystem is among the twenty most endangered ecosystems in the United States. The DEIS compares this remnant with other remnants only to denigrate its conservation value and justify the proposed destruction of some 72% of this rem- nant, and severe fragmentation of another 14%. But it is silent on the importance of large, unfragmented habitat for conservation of biodiversity, and the fact that the project contains about the fourth largest of eight remaining large contiguous rem- nants of lowland dry forest on Maui. Moreover, the remnant is some 4 miles from Pu`u O Kali, which contains a number of listed endangered plant species, and it is likely that it could serve as critical habitat in their recovery. All of these eight rem- nants of this endangered ecosystem should be preserved and dedicated to restora- tion efforts. General Comments Lowland Hawaiian dry forest is an endangered ecosystem. Government and private ac- tions have allowed this ecosystem to be reduced to amounts and states of degradation that threaten its long-term existence. -
Plant Group 2009
1 Erythrina sandwicensis Demography and Spatial Patterns of Erythrina gall wasp, Quadratichus erythrinae Infestation in Waikoloa, Hawai‘i Couch, C.S., J.S. Simonis, R.Q. Thomas, M. Manuel, D. Faucette, J.P. Sparks Abstract: Hawai‘i’s tropical dry forests are unique and highly endangered ecosystems that are currently being degraded by human development and invasive species. The Wiliwili tree, Erythrina sandwicensis (Fabaceae), a dominant species in Hawaiian tropical dry forests is now critically threatened due to the destructive impacts of invasive species, in particular the Erythrina gall wasp, Quadratichus erythrinae (Hymenoptera: Eulophidae). Here, we investigated the spatial and size distribution patterns of E. sandwicensis and potential effects of Q. erythrinae on population demographics by surveying a 310 ha parcel of dry forest in Waikoloa, Hawai‘i. This population of E. sandwicensis is comprised of 119 live trees, all of which are large adults that were spatially clumped to a radius of 400 meters.. In addition, the level of infestation of individual trees by Q. erythrinae was highly spatially autocorrelated, with the greatest correlation occurring within 100 m. Individual trees with higher gall wasp infestation had less tree leaf cover and a lower probability of seeds being present. The results of this study demonstrate that the largest population of E. sandwicensis on Hawai‘i is currently threatened by an invasive insect that alters the ability of trees to photosynthesize and decreases reproductive output. The clumped distribution of individuals likely facilitates the spread of the gall wasp but may allow for spatially focused conservation efforts. Thus a greater understanding of the severity of 2 invasive species impacts on plant physiology and reproductive fitness is necessary for the proper management of E. -
Notes on Alien and Native Bees (Hymenoptera: Apoidea) from the Hawaiian Islands1
Records of the Hawaii Biological Survey for 2012. Edited by Neal L. Evenhuis & Lucius G. Eldredge. Bishop Museum Occasional Papers 114: 61 –65 (2013) Notes on alien and native bees (Hymenoptera : Apoidea ) from the Hawaiian Islands 1 KARl N. M AGNACCA 2,3 Hawai‘i Division of Forestry and Wildlife, c/o University of Hawai‘i–Hilo, Dept. of Biology, 200 W. Kawili St., Hilo, Hawaii 96720, USA; email: [email protected] JASoN GiBBS Cornell University, Department of Entomology, 3119 Comstock Hall, Ithaca, New York, 14853, USA; email: [email protected] SAM dRoeGe U.S. Geological Survey, Patuxent Wildlife Research Center, 11510 American Holly Drive, Laurel, Maryland 20708-4017, USA; email: [email protected]) Four introduced bees are recorded from the Hawaiian islands for the first time, along with notes on previously recorded species, including rediscovery of the endemic Hylaeus anom - alus (Perkins, 1899). Both of the new Lasioglossum species are relatively recent arrivals, but their precise date of introduction is not known because the alien Lasioglossum are often ignored by collectors and are poorly represented in collections. it had been assumed that all were L. impavidum (Sandhouse, 1924), which has been present in the islands since at least 1957 (Beardsley 1958, Beardsley 1959). A recent survey of o‘ahu lowland disturbed sites by Sd found three distinct species – L. impavidum , L. imbrex Gibbs, 2010, and L. microlepoides (ellis, 1914) – prompting a review of earlier specimens. Unless otherwise noted, specimens listed below were collected by KNM; specimens are deposited at the Bishop Museum (BPBM) and University of Hawai‘i–Mānoa insect Museum (UHiM).