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SHORT-TAILED SHEARWATER Ardenna Tenuirostris Non-Breeding Visitor, Occasional Migrant Monotypic
SHORT-TAILED SHEARWATER Ardenna tenuirostris non-breeding visitor, occasional migrant monotypic The Short-tailed Shearwater breeds on islands off S and SE Australia in Nov- May, disperses northward through the W Pacific to the Bering Sea in May-Aug, and migrates rapidly southwestward in large flights across the central Pacific, back the breeding grounds, in Sep-Nov (King 1967, Harrison 1983, AOU 1998, Howell 2012). In the Hawaiian Islands, large numbers have been recorded during well-defined pulses in fall migration, and several sight observations of one to a few birds suggest a smaller passage in spring. The Short-tailed Shearwater is extremely difficult to separate from the similar Sooty Shearwater in the field (see Sooty Shearwater), especially when viewing isolated individuals (King 1970); thus, confirmation of the spring passage with specimen or photographic evidence is desirable. Short-tailed Shearwater was placed in genus Puffinus until moved to Ardenna by the AOU (2016). At sea, Short-tailed Shearwaters were recorded in large numbers during 2002 HICEAS, with 37,874 individuals observed on 52 of 163 observing days from W of Kure to S of Oahu (Rowlett 2002; HICEAS data); they were observed from 1 Sep to 14 Nov. Over 1,000 birds were recorded on each of seven dates, with a large peak of >28,000 recorded 13-22 Sep 2002 between Midway and Lisianski and a smaller peak of >4,000 recorded 30 Oct-14 Nov between Laysan and Kaua'i. All birds were flying SSW in concentrated groups. In contrast to Sooty Shearwater, Short-taileds were clearly more abundant in Northwestern than Southeastern Hawaiian Island waters during fall passage; only 66 birds were recorded on 3 of 35 dates during this period off the Southeastern Hawaiian Islands. -
Summary of 2016 Reef Fish Surveys Around Kahoolawe Island 1
doi:10.7289/V5/DR-PIFSC-17-011 Summary of 2016 Reef Fish Surveys around Kahoolawe Island 1 Results and information presented here summarize data gathered by the Coral Reef Ecosystem Program (CREP) of NOAA’s Pacific Islands Fisheries Science Center and partners during 2 days of reef fish and habitat surveys around Kahoolawe Island in July/August 2016. Surveys were conducted as part of the NOAA National Coral Reef Monitoring Program. Surveys were conducted using a standard sampling design and method implemented by NOAA’s Pacific Reef Assessment and Monitoring Program (Pacific RAMP) since 2009. In brief, pairs of divers record numbers, sizes, and species of fishes inside adjacent 15m-diameter ‘point- count’ cylinders and estimate benthic cover by functional groups (e.g. ‘coral’, ‘sand’). Because it is unpopulated and protected, Kahoolawe is an important reference location in in the main Hawaiian Islands and may also be a significant source of larvae and fish recruits for other parts of Maui-nui and perhaps beyond. Therefore, CREP hopes to routinely survey Kahoolawe reefs during future monitoring efforts. However, as 2016 was the first year for Kahoolawe surveys, we have a relatively small sample size there - 24 sites - in comparison to other Main Hawaiian Islands (MHI: between 107 and 257 survey sites per island). Main conclusions and observations: • Reef fish biomass was high at most sites we visited in Kahoolawe, with mean island-wide biomass higher than at any other of the MHI, although only marginally higher than at Niihau. Biomass tended to be slightly higher at sites along the southern section of the island. -
Demartini NWHI Overview for CRSAW (Feb 1
NOWRAMP Overview Ed DeMartini NOAA Fisheries, PIFSC • Objectives • Design & Status of Surveys • Major Patterns Northwestern Hawaiian Islands 99 9 9 99 9 9 9 9 NWHI Survey Objectives • Qualitative reconnaissance of ichthyofauna; describe relative abundance, assemblage structure • Initial quantitative assessment of both economic and ecologically interacting resources (corals, algae, macrobenthos as well as fishes); to provide baseline characterization of biota • Subsequent monitoring of target taxa at select representative stations; to enable detection of major changes over decadal time frame Summary of Design Elements • Develop sampling and analysis designs; standardize data collection protocols – size- and species/taxon- specific tallies per unit area • graded bins: by cm (< 5 cm), by 5 cm (6-50 cm), …by 25 cm (> 100 cm TL) – station(=dive): 3, 25-m long x 4- or 8- m wide belt transects, plus 4, 10- m radius (5-min) SPCs, apportioned among 3 divers • belts: total 600 m2 area for “large” (> 20 cm Total Length, TL) fishes • belts: total 300 m2 area for “small” (< 20 cm TL) fishes • SPCs: total @ 1257 m2 area (fish > 25 cm TL only) – followed by @ 3,000 m2 Roving Diver Survey • Analysis Design – abundance (N, biomass) for baseline assessment – density for monitoring temporal change – stratified by major habitat within reef (eg, fore-, back-reef, lagoonal patch at atolls) Sampling & Analysis Design Summary (cont’d) – at least 50% hard substrate – number of stations proportional to reef-area (and variance of stratum) – all sampleable reef quadrants (emphasis on leeward for monitoring) – distribute among-observer bias (< 15%) across stations and tasks – control for seasonality (eg, in recruitment) by design • differs among NWHI and other reef-systems NOWRAMP Cruise-Effort • 5-cruise baseline assessment • 25-mo period from Sep 00 to Oct 02 – Sep-Oct 00: NOAA’s Townsend Cromwell (TC00-10) & R/V Rapture – Sep 01: Cromwell (TC01-11); FFS, Maro Reef – Sep-Oct 02: Cromwell (TC02-07) & Rapture • Single monitoring cruise thus far – Jul-Aug 03: Oscar E. -
Geology of Hawaii Reefs
11 Geology of Hawaii Reefs Charles H. Fletcher, Chris Bochicchio, Chris L. Conger, Mary S. Engels, Eden J. Feirstein, Neil Frazer, Craig R. Glenn, Richard W. Grigg, Eric E. Grossman, Jodi N. Harney, Ebitari Isoun, Colin V. Murray-Wallace, John J. Rooney, Ken H. Rubin, Clark E. Sherman, and Sean Vitousek 11.1 Geologic Framework The eight main islands in the state: Hawaii, Maui, Kahoolawe , Lanai , Molokai , Oahu , Kauai , of the Hawaii Islands and Niihau , make up 99% of the land area of the Hawaii Archipelago. The remainder comprises 11.1.1 Introduction 124 small volcanic and carbonate islets offshore The Hawaii hot spot lies in the mantle under, or of the main islands, and to the northwest. Each just to the south of, the Big Island of Hawaii. Two main island is the top of one or more massive active subaerial volcanoes and one active submarine shield volcanoes (named after their long low pro- volcano reveal its productivity. Centrally located on file like a warriors shield) extending thousands of the Pacific Plate, the hot spot is the source of the meters to the seafloor below. Mauna Kea , on the Hawaii Island Archipelago and its northern arm, the island of Hawaii, stands 4,200 m above sea level Emperor Seamount Chain (Fig. 11.1). and 9,450 m from seafloor to summit, taller than This system of high volcanic islands and asso- any other mountain on Earth from base to peak. ciated reefs, banks, atolls, sandy shoals, and Mauna Loa , the “long” mountain, is the most seamounts spans over 30° of latitude across the massive single topographic feature on the planet. -
Seed Ecology Iii
SEED ECOLOGY III The Third International Society for Seed Science Meeting on Seeds and the Environment “Seeds and Change” Conference Proceedings June 20 to June 24, 2010 Salt Lake City, Utah, USA Editors: R. Pendleton, S. Meyer, B. Schultz Proceedings of the Seed Ecology III Conference Preface Extended abstracts included in this proceedings will be made available online. Enquiries and requests for hardcopies of this volume should be sent to: Dr. Rosemary Pendleton USFS Rocky Mountain Research Station Albuquerque Forestry Sciences Laboratory 333 Broadway SE Suite 115 Albuquerque, New Mexico, USA 87102-3497 The extended abstracts in this proceedings were edited for clarity. Seed Ecology III logo designed by Bitsy Schultz. i June 2010, Salt Lake City, Utah Proceedings of the Seed Ecology III Conference Table of Contents Germination Ecology of Dry Sandy Grassland Species along a pH-Gradient Simulated by Different Aluminium Concentrations.....................................................................................................................1 M Abedi, M Bartelheimer, Ralph Krall and Peter Poschlod Induction and Release of Secondary Dormancy under Field Conditions in Bromus tectorum.......................2 PS Allen, SE Meyer, and K Foote Seedling Production for Purposes of Biodiversity Restoration in the Brazilian Cerrado Region Can Be Greatly Enhanced by Seed Pretreatments Derived from Seed Technology......................................................4 S Anese, GCM Soares, ACB Matos, DAB Pinto, EAA da Silva, and HWM Hilhorst -
Incidence and Evaluation of a New Rust Disease on Myrtaceae in Hawaii
Incidence and Evaluation of a New Rust Disease on Myrtaceae in Hawaii: Puccinia psidii Winter, Guava Rust Anne Marie LaRosa1 and Rob Hauff2 1USDA Forest Service, Institute of Pacific Islands Forestry 2Hawaii State Department of Land and Natural Resources, Division of Forestry and Wildlife Background Related Surveys and Research Figure 1. Ohia seedling with pustules. Figure 2. Rose apple dieback caused by P. psidii. Distribution: The rust disease, Puccinia psidii Winter, or guava rust, was originally Complimenting the forest survey, the Hawaii Agricultural Research Center is carrying described in 1884 from infections on guava in Brazil. Until 2005 this pathogen was out a nursery survey for P. psidii. Nurseries on all of the main islands that provide unknown outside the Neotropics and the state of Florida. It was first detected in seedlings to forestry and conservation are being targeted. Data such as host species, Hawaii in the spring of 2005 on ohia-lehua (Metrosideros polymorpha Gaud) and disease severity, and host species growing in adjacent natural areas are being has since spread from Oahu to all major Hawaiian Islands (Killgore and Heu, 2005). collected. Host Range: Puccinia psidii has an unusually broad host range for a rust. Other related work on P. psidii includes molecular work conducted by the University of Worldwide, the host range currently includes 21 genera and 72 species of Hawaii. Dr. Zhong is analyzing genetic material to characterize the disease in Hawaii Myrtaceae, including such common tropical species as Eucalyptus and guava and comparing it to DNA samples from Brazil and Florida. Disease material from the (Simpson and others, 2006). -
(Rattus Spp. and Mus Musculus) in The
CHAPTER SIX: CONCLUSIONS Aaron B. Shiels Department of Botany University of Hawaii at Manoa 3190 Maile Way Honolulu, HI. 96822 173 Along with humans, introduced rats (Rattus rattus, R. norvegicus, and R. exulans) and mice (Mus musculus) are among the most invasive and widely distributed mammals on the planet; they occur on more than 80% of the world‘s islands groups (Atkinson 1985; Towns 2009). By incorporating modern technology, such as aerial broadcast of rodenticides, the number of islands where invasive rodents can be successfully removed has recently increased (Howald et al. 2007). However, successful rat and mouse eradication on relatively large (> 5000 ha) or human-inhabited islands such as the main Hawaiian Islands rarely occurs (Howald et al. 2007) despite large sums of money and research efforts annually to combat invasive rodent problems (see Chapter 1 section ―Rat history in Hawaii‖; Tobin et al. 1990). Therefore, it is highly unlikely that invasive rats and mice will be eradicated from relatively large, human-occupied islands such as Oahu in the near or distant future (Howald et al. 2007); and accepting this may be a first step towards increasing the likelihood of native species conservation in archipelagos like Hawaii where introduced rodents have established. Determining which invasive rodent species are present at a given site is important because the risks that some rodent species pose to particular (prey) species and/or habitats differ from those posed by other rodent species. Two sympatric species cannot occupy the same niche indefinitely, in a stable environment (Gause 1934), which may partly explain why some rodent species may not occur where others are present (Harper 2006). -
Photographing the Islands of Hawaii
Molokai Sea Cliffs - Molokai, Hawaii Photographing the Islands of Hawaii by E.J. Peiker Introduction to the Hawaiian Islands The Hawaiian Islands are an archipelago of eight primary islands and many atolls that extend for 1600 miles in the central Pacific Ocean. The larger and inhabited islands are what we commonly refer to as Hawaii, the 50 th State of the United States of America. The main islands, from east to west, are comprised of the Island of Hawaii (also known as the Big Island), Maui, Kahoolawe, Molokai, Lanai, Oahu, Kauai, and Niihau. Beyond Niihau to the west lie the atolls beginning with Kaula and extending to Kure Atoll in the west. Kure Atoll is the last place on Earth to change days and the last place on Earth to ring in the new year. The islands of Oahu, Maui, Kauai and Hawaii (Big Island) are the most visited and developed with infrastructure equivalent to much of the civilized world. Molokai and Lanai have very limited accommodation options and infrastructure and have far fewer people. All six of these islands offer an abundance of photographic possibilities. Kahoolawe and Niihau are essentially off-limits. Kahoolawe was a Navy bombing range until recent years and has lots of unexploded ordinance. It is possible to go there as part of a restoration mission but one cannot go there as a photo destination. Niihau is reserved for the very few people of 100% Hawaiian origin and cannot be visited for photography if at all. Neither have any infrastructure. Kahoolawe is photographable from a distance from the southern shores of Maui and Niihau can be seen from the southwestern part of Kauai. -
Kaiser Permanente Lanai and Molokai Providers and Locations Directory
Lanai and Molokai Providers and Locations Directory kp.org Kaiser Permanente Your medical care We have a lot to offer you — and we don’t want you to miss any of it. One of the best ways to get the most from your Kaiser Permanente coverage is to become familiar with your benefits and how your health plan works for you. The following information can help you on your road to better health. Primary Care Providers This directory shows you where our primary care physicians and providers are located. We strongly encourage you to choose a primary care physician who will oversee and coordinate all aspects of your medical care, including specialist visits and hospitalizations. Call the office of your choice to schedule an appointment. Because we want you to be happy with your choice, you are free to change your doctor at any time. Self-Referrals to Affiliated Providers You don’t need a referral to make appointments for the following services and departments within our network of providers: Behavioral Health Services (Mental Health outpatient care) Eye examinations for glasses and contact lenses Family Medicine Health Education Internal Medicine Obstetrics and Gynecology Occupational Health Services Mental Health outpatient care is provided on a self-referral basis. For help at any time please call the Behavioral Health Call Center at 1-888-945-7600, Monday through Friday, 8 a.m. to 5 p.m. 2 Your Introduction to Kaiser Permanente Your medical care Specialty Care Your doctor will refer you to a specialist when it’s medically necessary. In some cases, that may mean recommending you get treated on Oahu where you’ll be cared for by a team of physicians who have access to facilities and equipment that may not be available on your island. -
Recovery Plan for Tyoj5llllt . I-Bland Plants
Recovery Plan for tYOJ5llllt. i-bland Plants RECOVERY PLAN FOR MULTI-ISLAND PLANTS Published by U.S. Fish and Wildlife Service Portland, Oregon Approved: Date: / / As the Nation’s principal conservation agency, the Department of the Interior has responsibility for most ofour nationally owned public lands and natural resources. This includes fostering the wisest use ofour land and water resources, protecting our fish and wildlife, preserving the environmental and cultural values ofour national parks and historical places, and providing for the enjoyment of life through outdoor recreation. The Department assesses our energy and mineral resources and works to assure that their development is in the best interests ofall our people. The Department also has a major responsibility for American Indian reservation communities and for people who live in island Territories under U.S. administration. DISCLAIMER PAGE Recovery plans delineate reasonable actions that are believed to be required to recover and/or protect listed species. Plans are published by the U.S. Fish and Wildlife Service, sometimes prepared with the assistance ofrecovery teams, contractors, State agencies, and others. Objectives will be attained and any necessary funds made available subject to budgetary and other constraints affecting the parties involved, as well as the need to address other priorities. Costs indicated for task implementation and/or time for achievement ofrecovery are only estimates and are subject to change. Recovery plans do not necessarily represent the views nor the official positions or approval ofany individuals or agencies involved in the plan formulation, otherthan the U.S. Fish and Wildlife Service. They represent the official position ofthe U.S. -
Topographic History of the Maui Nui Complex, Hawai'i, and Its Implications for Biogeography1
Topographic History ofthe Maui Nui Complex, Hawai'i, and Its Implications for Biogeography 1 Jonathan Paul Price 2,4 and Deborah Elliott-Fisk3 Abstract: The Maui Nui complex of the Hawaiian Islands consists of the islands of Maui, Moloka'i, Lana'i, and Kaho'olawe, which were connected as a single landmass in the past. Aspects of volcanic landform construction, island subsi dence, and erosion were modeled to reconstruct the physical history of this complex. This model estimates the timing, duration, and topographic attributes of different island configurations by accounting for volcano growth and subsi dence, changes in sea level, and geomorphological processes. The model indi cates that Maui Nui was a single landmass that reached its maximum areal extent around 1.2 Ma, when it was larger than the current island of Hawai'i. As subsi dence ensued, the island divided during high sea stands of interglacial periods starting around 0.6 Ma; however during lower sea stands of glacial periods, islands reunited. The net effect is that the Maui Nui complex was a single large landmass for more than 75% of its history and included a high proportion of lowland area compared with the contemporary landscape. Because the Hawaiian Archipelago is an isolated system where most of the biota is a result of in situ evolution, landscape history is an important detertninant of biogeographic pat terns. Maui Nui's historical landscape contrasts sharply with the current land scape but is equally relevant to biogeographical analyses. THE HAWAIIAN ISLANDS present an ideal logic histories that can be reconstructed more setting in which to weigh the relative influ easily and accurately than in most regions. -
Field Instructions for The
FIELD INSTRUCTIONS FOR THE INVENTORY OF THE PACIFIC ISLANDS 2013 Hawaii Edition Forest Inventory and Analysis Program Pacific Northwest Research Station USDA Forest Service THIS MANUAL IS BASED ON: FOREST INVENTORY AND ANALYSIS NATIONAL CORE FIELD GUIDE FIELD DATA COLLECTION PROCEDURES FOR PHASE 2 PLOTS VERSION 5.1 TABLE OF CONTENTS 1 INTRODUCTION ........................................................................................................................................................................ 1 1.1 PURPOSES OF THIS MANUAL ................................................................................................................................................... 1 1.2 ORGANIZATION OF THIS MANUAL .......................................................................................................................................... 1 1.2.1 UNITS OF MEASURE ................................................................................................................................................................. 2 1.2.2 GENERAL DESCRIPTION ............................................................................................................................................................ 2 1.2.3 PLOT SETUP .............................................................................................................................................................................. 3 1.2.4 PLOT INTEGRITY ......................................................................................................................................................................