The Following Tree Seedlings Are Available to Order from the State of Hawaii Division of Forestry and Wildlife, State Tree Nursery
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1151CIRC.Pdf
CIRCULAR 153 MAY 1967 OBSERVATIONS on SPECIES of CYPRESS INDIGENOUS to the UNITED STATES Agricultural Experiment Station AUBURN UNIVERSIT Y E. V. Smith, Director Auburn, Alabama CONTENTS Page SPECIES AND VARIETIES OF CUPRESSUS STUDIED 4 GEOGRAPHIC DISTRIBUTION-- 4 CONE COLLECTION 5 Cupressus arizonica var. arizonica (Arizona Cypress) 7 Cupressus arizonica var. glabra (Smooth Arizona Cypress) 11 Cupressus guadalupensis (Tecate Cypress) 11 Cupressus arizonicavar. stephensonii (Cuyamaca Cypress) 11 Cupressus sargentii (Sargent Cypress) 12 Cupressus macrocarpa (Monterey Cypress) 12 Cupressus goveniana (Gowen Cypress) 12 Cupressus goveniana (Santa Cruz Cypress) 12 Cupressus goveniana var. pygmaca (Mendocino Cypress) 12 Cupressus bakeri (Siskiyou Cypress) 13 Cupressus bakeri (Modoc Cypress) 13 Cupressus macnabiana (McNab Cypress) 13 Cupressus arizonica var. nevadensis (Piute Cypress) 13 GENERAL COMMENTS ON GEOGRAPHIC VARIATION ---------- 13 COMMENTS ON STUDYING CYPRESSES 19 FIRST PRINTING 3M, MAY 1967 OBSERVATIONS on SPECIES of CYPRESS INDIGENOUS to the UNITED STATES CLAYTON E. POSEY* and JAMES F. GOGGANS Department of Forestry THERE HAS BEEN considerable interest in growing Cupressus (cypress) in the Southeast for several years. The Agricultural Experiment Station, Auburn University, was the first institution in the Southeast to initiate work on the cy- presses in 1937, and since that time many states have introduced Cupressus in hope of finding a species suitable for Christmas tree production. In most cases seed for trial plantings were obtained from commercial dealers without reference to seed source or form of parent tree. Many plantings yielded a high proportion of columnar-shaped trees not suitable for the Christmas tree market. It is probable that seed used in Alabama and other Southeastern States came from only a few trees of a given geo- graphic source. -
Handbook Publication.Pub
Table of Contents Maui County’s Landscape and Gardening Handbook Xeriscaping in Maui County ................................................................. 1 Planning and Design................................................................................................................. 1 Hydro-zones.............................................................................................................................. 1 Plant Selection and the Maui jkCounty Planting Zones............................................................ 2 Soil Preparation ........................................................................................................................ 4 Mulching.................................................................................................................................... 5 Irrigation .................................................................................................................................... 5 Maintenance ............................................................................................................................. 7 Other Interesting Techniques for the Ambitious ..................................... 8 Xeriscape Ponds....................................................................................................................... 8 Aquaponics in the Backyard ..................................................................................................... 9 Water Polymer Crystals ........................................................................................................... -
Full Article
Volume 20: 29–33 ELOPEA Publication date: 16 February 2017 T dx.doi.org/10.7751/telopea11338 Journal of Plant Systematics plantnet.rbgsyd.nsw.gov.au/Telopea • escholarship.usyd.edu.au/journals/index.php/TEL • ISSN 0312-9764 (Print) • ISSN 2200-4025 (Online) Lectotypification of Mimosa pubescens Vent. (Fabaceae, Mimosoideae) Phillip G Kodela and Peter G Wilson National Herbarium of New South Wales, The Royal Botanic Gardens & Domain Trust, Mrs Macquaries Rd, Sydney, NSW 2000, Australia. [email protected]; [email protected] Abstract A lectotype is here designated for Mimosa pubescens Vent., the basionym of the Australian species Acacia pubescens (Vent.) R.Br. Introduction Acacia pubescens (Vent.) R.Br. has a restricted distribution in the greater Sydney region of New South Wales (see Tame 1992, Tindale and Kodela 2001, Kodela and Harden 2002, Kodela 2016, OEH 2016), and is listed as a Vulnerable species (OEH 2016). The basionym of Acacia pubescens, Mimosa pubescens, was originally published by Étienne Ventenat in the first volume of his work Jardin de la Malmaison (Ventenat 1803) that celebrated the collection of interesting plants from around the world in cultivation at the home of the Empress Josephine. Lack (2004: 35) notes that the number of Australian plants described in this work was “remarkably high” considering that the continent was, at that time, still largely unknown. The detailed descriptions were accompanied by fine illustrations by the famous botanical artist Redouté. At the time of compilation of the Acacia treatment in the Flora of Australia, no type specimen had been located (Tindale and Kodela 2001) and it was later suggested that the species could have been lectotypified on the plate in the protologue (Fig. -
Tree Spacing Is Per the City and County of Honolulu, Department of Parks and Recreation, Division of Urban Forestry - Street Tree Specifications
Recommended Industry Standard Plant Spacing Guidelines TREES: Canopy Spread Street Tree No. Common Botanical Small Medium Large Height Spacing WRA Comments 1 `A`ali`i Dodonaea viscosa X < 30' 25 NL 2 `Ohai Ali`i Caesalpinia pulcherrima X < 20' 25 5 3 `Ohi`a Lehua Metrosideros polymorpha X 80' - 100' 40 NL 4 Alahe`e Psydrax odorata X 3' - 30' 25 NL 5 Autograph Clusia rosea X < 30' 60 5 6 Beach Heliotrope Tournefortia argentea X X 15' - 35' 40 -1 7 Breadfruit Artocarpus altilis X 60' N/A -12 8 Brown Pine Podocarpus elatus X 100' - 125' N/A -2 25' o.c. 9 Carrotwood Cupaniopsis anacardioides X 25' - 40' 40 9 10 Coral Erythrina crista-galli X < 30' 40 6 11 Crape Myrtle Lagerstroemia indica X X < 30' 25 6 12 False Olive Cassine orientalis X < 30' 40 -1 13 False Sandalwood (Naio) Myoporum sandwicense X 30' - 60' N/A NL 60' o.c. 14 Fern Podocarpus Afrocarpus gracilior X 20' - 40' 40 0 15 Geiger (Haole Kou) Cordia sebestena X < 30' N/A -1 40' o.c. 16 Geometry Bucida buceras X 45' - 60' 40 -3 17 Giant Crape Myrtle Lagerstroemia speciosa X 30' - 80' 60 -4 18 Gold tree Roseodendron donnell-smithii X 60' - 90' 85 -4 Handroanthus ochracea subsp. 19 Golden Trumpet neochrysantha X 40' - 60' 60 -3 20 Hala Pandanus tectorius X X < 35' N/A NL 25' o.c. 21 Hau Hibiscus tiliaceus X X < 35' N/A NL 40' o.c. 22 Hau (Variegated) Hibiscus tiliaceus forma X < 30' 25 NL 23 Ho`awa Pittosporum hosmeri X < 30' 25 NL 24 Hong Kong Orchid Bauhinia xblakeana X 25' - 35' 40 -7 Recommended Industry Standard Plant Spacing Guidelines TREES: Canopy Spread Street Tree No. -
Impacts of Alien Land Arthropods and Mollusks on Native Plants and Animals in Hawaii
7. IMPACTS OF ALIEN LAND ARTHROPODS AND MOLLUSKS ON NATIVE PLANTS AND ANIMALS IN HAWAIfI Francis G. Howarth ABSTRACT Over 2,000 alien arthropod species and about 30 alien non-marine mollusks are established in the wild in Hawai'i, While the data are too meager to assess fully the impacts of any of these organisms on the na- tive biota, the documentation suggests several areas of critical concern. Alien species feed directly on na- tive plants or their products, thus competing with na- tive herbivores and affecting host plants. Alien pred- ators and parasites critically reduce the populations of many native species and seriously deplete the food resources of native predators. Some immigrant species spread diseases that infect elements of the native bio- ta. Others are toxic to native predators. There is also competition for other resources, such as nesting and resting sites. Even apparently innocuous intro- duced species may provide food for alien predators, thus keeping predator populations high with an atten- dant greater impact on native prey. Control measures targeted at alien pests may be hazardous to natives. Mitigative measures must be based on sound research and firmer understanding of the complex interactions and dynamics of functioning ecosystems. Strict quarantine procedures are cost effective in preventing or delaying the establishment of potential pests. Strict control or fumigation is needed for nonessential importations (such as cow chips, Christmas trees, and flowers in bulk). Improved review of introductions for biological control is required in order to prevent repeating past mistakes. Biocontrol introductions must be used only for bona fide pests and used in native ecosystems only in special circumstances. -
Eucalyptus Robusta NZ Myrtaceae Key - Online Edition Eucalyptus Robusta Sm
11/16/2020 Eucalyptus robusta NZ Myrtaceae Key - Online edition Eucalyptus robusta Sm. Common Names swamp mahogany, swamp messmate Origin Australia: coastal New South Wales to south-eastern Queensland. Cultivation In New Zealand predominantly cultivated for timber or amenity; very occasionally naturalised from nearby specimens. Distribution Mainly in northern coastal and lowland areas in the North Island of New Zealand. Distinguishing Features Tree with thick, fibrous, spongy, reddish-brown to grey-brown bark with deep longitudinal furrows, extending to the small branches. Mature leaves that are glossy, darker green on the upper side, paler beneath, strongly feather-veined. Long-stalked, spindle- or pear-shaped flower buds to 20 mm long and 9 mm wide, in clusters of 9–15. Fruit that are woody capsules, long-stalked, cylindrical to 18 mm long and 11 mm wide, with disc descending inside rim of capsule, and the three or four valve tips joined across the mouth of the capsule. Habit Tree to 30 m tall. Bark and Stem/Trunk Bark of main trunk thick, fibrous, spongy, reddish-brown to grey-brown, in elongated slabs with furrows between, extending to the small branches; ribbons absent. Hairs and adventitious roots absent. Young stems square in cross-section, sometimes winged. Leaves Mature leaves alternate, stalked, broadly lanceolate to ovate, feather-veined, tip pointed, base tapering to leaf stalk, glossy, dark green above and paler below, hairs absent, 85–170 mm long, 25–70 mm wide. Vein reticulation moderate to dense, main side-veins at a relatively wide angle to the midrib, intramarginal veins present just inside margin; oil glands usually inconspicuous; leaf stalk 15–30 mm long. -
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. -
Metrosideros Polymorpha Gaudich
Metrosideros polymorpha Gaudich. JAMES A. ALLEN Paul Smiths College, Paul Smiths, NY MYRTACEAE (MYRTLE FAMILY) Metrosideros collina (J.R. and G. Forst.) A. Gray subsp. polymorpha (Gaud.) Rock. (Little and Skolmen 1989). See also the extensive list of synonyms in Wagner and others (1990) Lehua, ‘ohi’a Metrosideros is a genus of about 50 species. With the excep- hybridization and genetic polymorphism is unknown (Wagner tion of one species found in South Africa, all grow in the and others 1990). Pacific from the Philippines, through Papua New Guinea, to The heartwood is reddish brown, heavy (specific gravity New Zealand and on high volcanic islands (Wagner and oth- of about 0.70), of fine and even texture, very hard, and strong. ers 1990). Five species occur in the Hawaiian Islands (Wag- Native Hawaiians used the wood extensively for construction, ner and others 1990). Metrosideros polymorpha is native to household implements, and carvings. Principal modern uses Hawaii, where it grows on all the main islands except Niihau include flooring, marine construction, pallets, fenceposts, and and Kahoolawe. It is the most abundant and widespread fuelwood. The wood’s limitations include excessive shrinkage M native tree in Hawaii (Adee and Conrad 1990) and grows in in drying, density, and the difficulty and expense of harvesting association with numerous species in both wet and relatively in low-volume stands (Adee and Conrad 1990, Little and Skol- dry forests. men 1989). Today, M. polymorpha is perhaps most highly val- Metrosideros polymorpha is a slow-growing, evergreen ued in Hawaii for uses in watershed protection, aesthetics, and species capable of reaching 24 to 30 m in height and about 1 m habitat for native birds, including several endangered species. -
Cook Pine) Aqueous Resin Extract Against Major Phytopathogens
MAY 2014 – JULY 2014, Vol. 4, No. 3; 2108-2112. E- ISSN: 2249 –1929 Journal of Chemical, Biological and Physical Sciences An International Peer Review E-3 Journal of Sciences Avail able online at www.jcbsc.org Section B: Biological Sciences CODEN (USA): JCBPAT Research Article Bio-Fungicide Potential of Araucaria Columnaris (Cook Pine) Aqueous Resin Extract Against Major Phytopathogens Saranya Devi. K* 1, J. Rathinamala 1 and S. Jayashree 2 1Department of Microbiology, Nehru Arts and Science College, Coimbatore, 2Department of Biotechnology, Nehru Arts and Science College, Coimbatore, Tamil Nadu, India. Received: 05 March 2014 ; Revised: 25 April 2014 ; Accepted: 03 May 2014 Abstract: Use of chemical fungicide to control plant diseases causes several adverse effects such as, development of resistance in the pathogen, residual toxicity, pollution to the environment etc. So an alternative way to overcome the usage of dreadful chemicals is very important. The use of plant extracts as biofungicide is one of the popular and effective method. Araucaria columnaris is a commonly seen ornamental plant known as Christmas tree. It’s a South African species, under the family Araucariaceae. Hence, in the present study, the plant resin extract was tested in-vitro against major plant pathogensby preliminary bioassay. It was found that up to 95% reduction of mycelium growth was observed against major phytopathogens such as Fusarium oxysporyum , Rhizoctonia sp, Cylindrocladium sp, Alternaria sp, and Colletrotricum sp., causing tomato wilt, damping off, foliage blight, and leaf blight diseases in economically important plants. Up to our knowledge it is the first report showing the antifungal activity of Araucaria columnaris resin as antifungal agent. -
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 ................................................................................................................................ -
Flying-Fox Dispersal Feasibility Study Cassia Wildlife Corridor, Coolum Beach and Tepequar Drive Roost, Maroochydore
Sunshine Coast Council Flying-Fox Dispersal Feasibility Study Cassia Wildlife Corridor, Coolum Beach and Tepequar Drive Roost, Maroochydore. Environmental Operations May 2013 0 | Page Table of Contents Introduction ................................................................................................................................ 2 Purpose ............................................................................................................................................... 2 Flying-fox Mitigation Strategies .......................................................................................................... 2 State and Federal Permits ................................................................................................................... 4 Roost Management Plan .................................................................................................................... 4 Risk ...................................................................................................................................................... 5 Flying-fox Dispersal Success in Australia ............................................................................................. 6 References .......................................................................................................................................... 7 Cassia Wildlife Corridor ................................................................................................................ 8 Background ........................................................................................................................................