Large Scale Multiplication of Casuarina Junghuhniana Miq
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The Effect of Lighting and Temperature on the Eggs and Hatchlings of Olive Ridley Turtles at Rushikulya, India a Thesis Submitte
The effect of lighting and temperature on the eggs and hatchlings of olive ridley turtles at Rushikulya, India A Thesis Submitted to The Manipal University In partial fulfillment for the degree of Master of Science in Wildlife Biology and Conservation 2008 By Divya Karnad Post-Graduate Program in Wildlife Biology & Conservation Centre for Wildlife Studies and National Centre for Biological Sciences UAS-GKVK Campus Bangalore – 500 065 ii iii To those who teach by example, especially my family, Arun and Sashirekha. iv EXECUTIVE SUMMARY The olive ridley turtle (Lepidochelys olivacea) nests both sporadically and en masse along the Indian Coast. Of the three mass nesting sites along the East coast of India, the Rushikulya rookery may currently have the most regular nesting population of olive ridley turtles and is therefore likely to play a key role in maintaining the Indian Ocean population of the species. The sporadic nesting site of Chennai is completely altered by human activity and represents a set of conditions completely different from those in Rushikulya. Olive ridley turtles in India are protected and have been studied for several years but detailed studies on factors affecting nesting and hatching have not been conducted. The present study examines the effect of temperature and lighting on egg and hatchling survival of the olive ridley turtle. The response of the hatchlings to different lighting regimes on the beach, as well as to specific combinations of wavelength and intensity of light was studied. Hatchlings responded to both intense point sources of light at Rushikulya as well as glows from hidden point sources. -
Nesting Site Studies of White-Bellied Sea Eagle (Haliaeetus Leucogaster Gmelin, 1788) Along Konkan Coast, Dist
Eco. Env. & Cons. 27 (February Suppl. Issue) : 2021; pp. (S108-S115) Copyright@ EM International ISSN 0971–765X Nesting site studies of White-bellied Sea Eagle (Haliaeetus leucogaster Gmelin, 1788) along Konkan Coast, Dist. Ratnagiri, M. S., India Aditi S. Neema1, B. Anjan Kumar Prusty2, Nikunj B. Gajera3 and Poonam N. Kurve4 1,4Department of Biodiversity, Wildlife Conservation and Management BN Bandodkar College of Science, Thane (Univ. of Mumbai), Building 6, Jnanadweepa, Chendani Bunder Road, Thane West, Thane 400 601, Maharashtra 2,3Environmental Impact Assessment Division, Gujarat Institute of Desert Ecology (GUIDE), Bhuj 370 040, Gujarat, India (Received 25 April, 2020; Accepted 12 August, 2020) ABSTRACT Nesting behaviour of White-bellied Sea Eagle has been meagerly studied though; the raptor is widely distributed along the coast of Maharashtra. Present study was carried out by conducting surveys for locating their nesting sites along coast of Ratnagiri district and 12 nests of White-bellied Sea Eagle Haliaeetus leucogaster at different sites along Velas to Dabhol were studied. Various ecological parameters such as nesting tree species, nesting tree height, nesting tree GBH, nest height, geo-coordinates, distance from coast, disturbance level were considered. WBSE was found to be most abundantly nesting (N =12) on Casuarina equisetifolia tree which, accounts to 83% of the total nesting trees and only 02 nests, just 17% of the total nesting trees studied, were on Sterculia foetida. In most cases, it was observed that WBSEs prefer nest trees with larger GBH as compared to same tree species of smaller girth. Location of nest from the supratidal mark was measured to study nesting preference about distance from the sea and we found that, the nearest nest was 30 m away from the coast and the farthest one was at a distance of around 900 m. -
Technical Guidelines for Reforestation at Ex-Coal-Mining Areas
Technical Guidelines for Reforestation at Ex-Coal-Mining Areas - Based on the outcomes of experimental reforestation activities at ex-coal-mining areas in South Kalimantan, Indonesia - Japan International Forestry Promotion and Cooperation Center (JIFPRO) March 2015 Technical Guidelines for Reforestation at Ex-Coal-Mining Areas - Based on the outcomes of experimental reforestation activities at ex-coal-mining areas in South Kalimantan, Indonesia - Eiichiro Nakama, Seiichi Ohta, Yasuo Ohsumi, Tokunori Mori and Satohiko Sasaki Japan International Forestry Promotion and Cooperation Center Fakhrur Razie, Hamdani Fauzi and Mahrus Aryadi Lambung Mangkurat University, Indonesia Japan International Forestry Promotion and Cooperation Center March 2015 Foreword During the past decades, deforestation and forest degradation continues especially in developing countries. According to the report of the Food and Agriculture Organization of the United Nation (FAO), approximately 13 million hectors of global forests have been lost annually due to forest land conversion to other land uses, forest fires and natural disasters, while reforestation and natural regeneration account for an increase of approx. 7.8 million hectors of forest cover. This means the net loss of global forest is estimated at 5.2 million hectors. Adverse impacts of forest conversion to farmland can be minimized as far as the land is properly used and managed in a sustainable manner. However, in some cases, problem soils are exposed and abandoned as degraded land. Deforestation by mining is a big issue these years. Problem soils such as strong acid soils and/or too much heavy metal soils appear at the ex-mining areas. In some cases it is too difficult to reforestate. -
National List of Vascular Plant Species That Occur in Wetlands 1996
National List of Vascular Plant Species that Occur in Wetlands: 1996 National Summary Indicator by Region and Subregion Scientific Name/ North North Central South Inter- National Subregion Northeast Southeast Central Plains Plains Plains Southwest mountain Northwest California Alaska Caribbean Hawaii Indicator Range Abies amabilis (Dougl. ex Loud.) Dougl. ex Forbes FACU FACU UPL UPL,FACU Abies balsamea (L.) P. Mill. FAC FACW FAC,FACW Abies concolor (Gord. & Glend.) Lindl. ex Hildebr. NI NI NI NI NI UPL UPL Abies fraseri (Pursh) Poir. FACU FACU FACU Abies grandis (Dougl. ex D. Don) Lindl. FACU-* NI FACU-* Abies lasiocarpa (Hook.) Nutt. NI NI FACU+ FACU- FACU FAC UPL UPL,FAC Abies magnifica A. Murr. NI UPL NI FACU UPL,FACU Abildgaardia ovata (Burm. f.) Kral FACW+ FAC+ FAC+,FACW+ Abutilon theophrasti Medik. UPL FACU- FACU- UPL UPL UPL UPL UPL NI NI UPL,FACU- Acacia choriophylla Benth. FAC* FAC* Acacia farnesiana (L.) Willd. FACU NI NI* NI NI FACU Acacia greggii Gray UPL UPL FACU FACU UPL,FACU Acacia macracantha Humb. & Bonpl. ex Willd. NI FAC FAC Acacia minuta ssp. minuta (M.E. Jones) Beauchamp FACU FACU Acaena exigua Gray OBL OBL Acalypha bisetosa Bertol. ex Spreng. FACW FACW Acalypha virginica L. FACU- FACU- FAC- FACU- FACU- FACU* FACU-,FAC- Acalypha virginica var. rhomboidea (Raf.) Cooperrider FACU- FAC- FACU FACU- FACU- FACU* FACU-,FAC- Acanthocereus tetragonus (L.) Humm. FAC* NI NI FAC* Acanthomintha ilicifolia (Gray) Gray FAC* FAC* Acanthus ebracteatus Vahl OBL OBL Acer circinatum Pursh FAC- FAC NI FAC-,FAC Acer glabrum Torr. FAC FAC FAC FACU FACU* FAC FACU FACU*,FAC Acer grandidentatum Nutt. -
Performance of Mesophytic Species Planted in the Coast of Char Kashem, Patuakhali, Bangladesh
Bangladesh J. Bot. 39(2): 245-247, 2010 (December) - Short communication PERFORMANCE OF MESOPHYTIC SPECIES PLANTED IN THE COAST OF CHAR KASHEM, PATUAKHALI, BANGLADESH MD GOLAM MOULA Bangladesh Forest Research Institute, Post Box No. 273, Chittagong 4000, Bangladesh Key words: Mesophytes, Coastal afforestation, Growth performance, Bangladesh Abstract Mesophytic species such as Acacia nilotica, Albizia labeck, Albizia procera, Casuarina equisetifolia, Pithocellobium dulche, Samanea saman and Thespesia populnea were raised in the western coast of Char Kashem under Patuakhali district of Bangladesh. After seven years of planting highest survivability was found in A. labeck followed by P. dulche, C. equisetifolia, S. saman, A. procera, A. nilotica and T. populnea. The mean maximum diameter at breast height was found in S. saman followed by C. equisetifolia, A. procera, A. labeck, P. dulche, A. nilotica and T. populnea. The maximum plant height was found in C. equisetifolia followed by S. saman, A. procera, T. populnea, A. nilotica, A. labeck and P. dulche indicating suitability of all the seven species for plantation at Char Kashem. Coastal afforestation in 1966 was primarily initiated to save lives and properties of the coastal dwellers from the devastating cyclones and tidal surges (Das and Siddiqi 1985) and secondarily to (i) reclamation and stabilization of newly accreted land and acceleration of further accretion, (ii) production of timber and fuel wood and (iii) creation of employment opportunity in the coastal areas (Saenger 1987). The coastal afforestation programme gained a momentum with the involvement of World Bank in 1975 (Imam 1982). Up to 2001 a total of 1,48,526 hectares of mangrove plantation has been established under different projects. -
Evaluation of International Provenance Trials of Casuarina Equisetifolia
ACRC100.book Page 1 Wednesday, June 23, 2004 1:42 PM Evaluation of International Provenance Trials of Casuarina equisetifolia K. Pinyopusarerk, A. Kalinganire, E.R. Williams and K.M. Aken Australian Tree Seed Centre CSIRO Forestry and Forest Products PO Box E4008 Kingston ACT 2604 Australia Australian Centre for International Agricultural Research Canberra 2004 Evaluation of international provenance trials of Casuarina equisetifolia K. Pinyopusarerk, A. Kalinganire, E.R. Williams and K.M. Aken ACIAR Technical Reports No 58e (printed version published in 2004) ACRC100.book Page 2 Wednesday, June 23, 2004 1:42 PM The Australian Centre for International Agricultural Research (ACIAR) was established in June 1982 by an Act of the Australian Parliament. Its mandate is to help identify agricultural problems in developing coun- tries and to commission collaborative research between Australia and developing country researchers in fields where Australia has a special research competence. Where trade names are used this constitutes neither endorsement of nor discrimination against any product by the Centre. ACIAR TECHNICAL REPORTS SERIES This series of publications contains technical information resulting from ACIAR-supported programs, projects and workshops (for which proceedings are not being published), reports on Centre-supported fact-finding studies, or reports on other useful topics resulting from ACIAR activities. Publications in the series are distributed internationally to a selected audience. © Australian Centre for International Agricultural Research, GPO Box 1571, Canberra, ACT 2601 K. Pinyopusarerk, A. Kalinganire, E.R. Williams and K.M. Aken 2004. Evaluation of international provenance trials of Casuarina equisetifolia. ACIAR Technical Report No. 58, 106p. ISBN 1 86320 440 7 (printed) ISBN 1 86320 441 5 (online) Cover design: Design One Solutions Cover photo by K. -
Thespesia Populnea (Milo) Left: Newly Opened Flower
April 2006 Species Profiles for Pacific Island Agroforestry ver. 2.1 www.traditionaltree.org Thespesia populnea (milo) Malvaceae (mallow family) badrirt (Palau); banalo (Northern Marianas); bang-beng (Yap); kilulo (Guam); mi‘o (Marquesas); milo (Hawai‘i, Mar- shall Islands, Samoa, Tonga); miro (Pitcairn Island); miro, ‘amae (Rarotonga, Society Islands); mulomulo (Fiji); panu (Kosrae); polo (Chuuk); pone (Pohnpei); purau (Tahiti); portia tree, seaside mahoe, Pacific rosewood, Indian tulip tree, cork tree, umbrella tree (English) J. B. Friday and Dana Okano photo: J. B. Friday B. J. photo: Milo tree on a beach in Lahaina, Maui, Hawai‘i. IN BRIEF Growth rate Moderate, 0.6–1 m/yr (2–3 ft/yr) for the first Distribution Coastal areas of the Indian and Pacific few years. Oceans; throughout Oceania. Main agroforestry uses Soil stabilization, windbreak. Size Small tree typically 6–10 m (20–33 ft) at maturity. Main uses Craftwood, ornamental. Habitat Tropical and warm subtropical, usually found at Yields Heartwood in 30+ years. sea level to 150 m (500 ft). Intercropping Compatible with many coastal species, al- Vegetation Associated with a wide range of coastal spe- though it requires full sun. cies. Invasive potential Has potential to become an invasive Soils Thrives on sandy coastal soils as well as volcanic, weed—should not be introduced into new areas. limestone, and rocky soils. INTRODUCTION Current distribution Milo (Thespesia populnea) is one of the most important trees Milo has been planted throughout the tropics and is natu- to Pacific Island peoples. The rich, dark wood is carved into ralized in tropical climates throughout the world from the beautiful bowls, tools, small canoes, and figures. -
Casuarina Spp.), an Invader of Coastal Florida, U.S.A
Journal of Coastal Research 27 3 485–492 West Palm Beach, Florida May 2011 Ecology and Management of Sheoak (Casuarina spp.), an Invader of Coastal Florida, U.S.A. G.S. Wheeler{, G.S. Taylor{, J.F. Gaskin1, and M.F. Purcell{{ www.cerf-jcr.org {USDA Agricultural Research {Australian Centre for 1USDA Agricultural Research {{USDA Agricultural Research Service Evolutionary Biology and Service Service Invasive Plant Research Biodiversity Northern Plains Agricultural Australian Biological Control Laboratory and School of Earth and Research Laboratory Laboratory 3225 College Avenue Environmental Sciences 1500 North Central Avenue CSIRO Entomology Fort Lauderdale, FL 33314, The University of Adelaide Sidney, MT 59270, U.S.A. 120 Meiers Road U.S.A. North Terrace, Adelaide, SA Indooroopilly, QLD 4068, 5005, Australia Australia ABSTRACT WHEELER, G.S.; TAYLOR, G.S.; GASKIN, J.F., and PURCELL, M.F., 2011. Ecology and management of sheoak (Casuarina spp.), an invader of coastal Florida, U.S.A. Journal of Coastal Research, 27(3), 485–492. West Palm Beach (Florida), ISSN 0749-0208. The Casuarina spp. are invasive plants in Florida that threaten biological diversity and beach integrity of coastal habitats. The trees include three species and their hybrids that aggressively invade riverine and coastal areas. Of the three species, C. equisetifolia and C. glauca are highly salt tolerant and widespread in coastal areas. The third species, C. cunninghamiana, invades riverine habitats. These species pose dangers to both the environment and public safety. The environmental damage includes interfering with nesting by endangered sea turtles, American crocodiles, and the rare swallow-tailed kite. Additionally, allelochemical leachates reduce germination and establishment of native vegetation. -
Glossy Black-Cockatoo
Glossy black-cockatoo Calyptorynchus lathami Yuyang (Wiradjuri) Photo: Chris Tzaros The glossy black-cockatoo may be confused with the red-tailed black-cockatoo, but it has more brownish-black plumage on the head, neck and underbody. Their body plumage is more dull black and not uniformly glossy. Also, adult females have much more yellow on the head and lack the yellow spotting on the body that red-tailed black-cockatoos have. Description Size: The glossy black-cockatoo of the Riverina is a medium-sized cockatoo. Plumage: Glossy black-cockatoos are generally black but have a blackish-brown head, neck and underparts with red or yellowish-red panels in the tail. Adult females have patches of yellow feathering on head and neck. Bill: They have a broad bulbous bill that is used for tearing apart the seed cones of sheoaks, their primary food source, and to create hollows in old trees for nesting. Call: Noisy squawks or creaky calls; wheezy ‘airr-riick’, ‘kee-aiirrk’, ‘airrek’. Quieter and less raucous than other black-cockatoos. Photo: Chris Tzaros Habitat Glossy black-cockatoos can be found in open forest and woodlands of the coast and the Great Dividing Range where stands of sheoak occur, such as black sheoak (Allocasuarina littoralis) and forest sheoak (A. torulosa). Inland, they feed on drooping sheoak (A. verticillata), broombush sheoak (A. diminuta) and mallee sheoak (A. gymnanthera). Belah (Casuarina cristata) is also utilised and may be a critical food source for some populations. The Riverina population is largely restricted to hills and low ridges where suitable stands of its food plant, the drooping sheoak, remain. -
Supplementary Material Saving Rainforests in the South Pacific
Australian Journal of Botany 65, 609–624 © CSIRO 2017 http://dx.doi.org/10.1071/BT17096_AC Supplementary material Saving rainforests in the South Pacific: challenges in ex situ conservation Karen D. SommervilleA,H, Bronwyn ClarkeB, Gunnar KeppelC,D, Craig McGillE, Zoe-Joy NewbyA, Sarah V. WyseF, Shelley A. JamesG and Catherine A. OffordA AThe Australian PlantBank, The Royal Botanic Gardens and Domain Trust, Mount Annan, NSW 2567, Australia. BThe Australian Tree Seed Centre, CSIRO, Canberra, ACT 2601, Australia. CSchool of Natural and Built Environments, University of South Australia, Adelaide, SA 5001, Australia DBiodiversity, Macroecology and Conservation Biogeography Group, Faculty of Forest Sciences, University of Göttingen, Büsgenweg 1, 37077 Göttingen, Germany. EInstitute of Agriculture and Environment, Massey University, Private Bag 11 222 Palmerston North 4474, New Zealand. FRoyal Botanic Gardens, Kew, Wakehurst Place, RH17 6TN, United Kingdom. GNational Herbarium of New South Wales, The Royal Botanic Gardens and Domain Trust, Sydney, NSW 2000, Australia. HCorresponding author. Email: [email protected] Table S1 (below) comprises a list of seed producing genera occurring in rainforest in Australia and various island groups in the South Pacific, along with any available information on the seed storage behaviour of species in those genera. Note that the list of genera is not exhaustive and the absence of a genus from a particular island group simply means that no reference was found to its occurrence in rainforest habitat in the references used (i.e. the genus may still be present in rainforest or may occur in that locality in other habitats). As the definition of rainforest can vary considerably among localities, for the purpose of this paper we considered rainforests to be terrestrial forest communities, composed largely of evergreen species, with a tree canopy that is closed for either the entire year or during the wet season. -
Australian Pine
FACT SHEET: AUSTRALIAN PINE Australian Pine Casuarina equisetifolia L. Beefwood family (Casuarinaceae) NATIVE RANGE Malaysia, southern Asia, Oceania and Australia DESCRIPTION Australian pine is a deciduous tree with a soft, wispy, pine-like appearance that can grow to 100 feet or more in height. Also known as ironwood, beefwood, she oak and horsetail tree, it bears a superficial resemblance to the conifer genus Pinus because of its small, round, cone-like fruits and its branchlets of scale-like leaves that look like pine needles. Its flowers are tiny, brown and wind-pollinated. The fruit is a nutlet about ½ inch in diameter that contains winged seeds. ECOLOGICAL THREAT Australian pine is fast-growing (5-10 feet per year), produces dense shade and a thick blanket of leaves and hard, pointed fruits, that completely covers the ground beneath it. Dense thickets of Australian pine displace native dune and beach vegetation, including mangroves and many other resident, beach-adapted species. Because its roots are capable of producing nitrogen through microbial associations, Australian pine can colonize nutrient-poor soils. Once established, it radically alters the light, temperature, and soil chemistry regimes of beach habitats, as it outcompetes and displaces native plant species and destroys habitat for native insects and other wildlife. Chemicals in the leaves of Australian pine may inhibit the growth of other plants underneath it. The ground below Australian pine trees becomes ecologically sterile and lacking in food value for native wildlife. Unlike native shrubbery, the thick, shallow roots of Australian pine make it much more susceptible to blow-over during high wind events, leading to increased beach and dune erosion and interference with the nesting activities of sea turtles. -
Supplementary Materialsupplementary Material
Supplementary Materials 10.1071/RJ16076_AC © CSIRO 2017 Supplementary Material: Rangeland Journal, 2017, 39(1), 85–95. Assessing the invasion threat of non-native plant species in protected areas using Herbarium specimen and ecological survey data. A case study in two rangeland bioregions in Queensland Michael R. NgugiA,B and Victor John NeldnerA AQueensland Herbarium, Department of Science Information Technology and Innovation, Mt Coot- tha Road, Toowong, Qld 4066, Australia. BCorresponding author. Email: [email protected] Table S1. List of native species in Cape York Peninsula and Desert Uplands bioregions Cape York Peninsula native Species Desert Uplands native Species Abelmoschus ficulneus Abelmoschus ficulneus Abelmoschus moschatus subsp. Tuberosus Abildgaardia ovata Abildgaardia ovata Abildgaardia vaginata Abildgaardia vaginata Abutilon arenarium Abrodictyum brassii Abutilon calliphyllum Abrodictyum obscurum Abutilon fraseri Abroma molle Abutilon hannii Abrophyllum ornans Abutilon leucopetalum Abrus precatorius L. subsp. precatorius Abutilon malvifolium Abutilon albescens Abutilon nobile Domin Abutilon auritum Abutilon otocarpum Abutilon micropetalum Abutilon oxycarpum Acacia armillata Abutilon oxycarpum Acacia armitii Abutilon oxycarpum var. incanum Acacia aulacocarpa Abutilon oxycarpum var. subsagittatum Acacia auriculiformis Acacia acradenia Acacia brassii Acacia adsurgens Acacia calyculata Acacia aneura F.Muell. ex Benth. var. aneura Acacia celsa Acacia aneura var. major Pedley Acacia chisholmii Acacia angusta Maiden