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One New Endemic Plant Species on Average Per Month in New Caledonia, Including Eight More New Species from Île Art (Belep Islan
CSIRO PUBLISHING Australian Systematic Botany, 2018, 31, 448–480 https://doi.org/10.1071/SB18016 One new endemic plant species on average per month in New Caledonia, including eight more new species from Île Art (Belep Islands), a major micro-hotspot in need of protection Gildas Gâteblé A,G, Laure Barrabé B, Gordon McPherson C, Jérôme Munzinger D, Neil Snow E and Ulf Swenson F AInstitut Agronomique Néo-Calédonien, Equipe ARBOREAL, BP 711, 98810 Mont-Dore, New Caledonia. BEndemia, Plant Red List Authority, 7 rue Pierre Artigue, Portes de Fer, 98800 Nouméa, New Caledonia. CHerbarium, Missouri Botanical Garden, 4344 Shaw Boulevard, Saint Louis, MO 63110, USA. DAMAP, IRD, CIRAD, CNRS, INRA, Université Montpellier, F-34000 Montpellier, France. ET.M. Sperry Herbarium, Department of Biology, Pittsburg State University, Pittsburg, KS 66762, USA. FDepartment of Botany, Swedish Museum of Natural History, PO Box 50007, SE-104 05 Stockholm, Sweden. GCorresponding author. Email: [email protected] Abstract. The New Caledonian biodiversity hotspot contains many micro-hotspots that exhibit high plant micro- endemism, and that are facing different types and intensities of threats. The Belep archipelago, and especially Île Art, with 24 and 21 respective narrowly endemic species (1 Extinct,21Critically Endangered and 2 Endangered), should be considered as the most sensitive micro-hotspot of plant diversity in New Caledonia because of the high anthropogenic threat of fire. Nano-hotspots could also be defined for the low forest remnants of the southern and northern plateaus of Île Art. With an average rate of more than one new species described for New Caledonia each month since January 2000 and five new endemics for the Belep archipelago since 2009, the state of knowledge of the flora is steadily improving. -
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. -
Short Communication
Biota Neotropica 20(1): e20190815, 2019 www.scielo.br/bn ISSN 1676-0611 (online edition) Short Communication A new synonym for Micropholis gardneriana (Sapotaceae) with complete description, anatomy and distribution notes Angélica Cândida Ferreira1* , Josiane Silva Araújo2 , Eduardo Bezerra de Almeida Jr3 & Carmen Silvia Zickel1 1Universidade Federal Rural de Pernambuco, Departamento de Biologia, Pós-graduação em Botânica, 52171-900, Recife, PE, Brasil 2Universidade Estadual do Piauí, Departamento de Biologia, 64280-000, Campo Maior, PI, Brasil 3Universidade Federal do Maranhão, Departamento de Biologia, 65080-805, São Luís, MA, Brasil *Corresponding author: Angélica Cândida Ferreira, e-mail: [email protected] Ferreira, A.C.; Araújo, J.S.; Almeida Jr., E.B.; Zickel, C.S. A new synonym for Micropholis gardneriana (Sapotaceae) with complete description, anatomy and distribution notes. Biota Neotropica. 20(1): e20190815. http://dx.doi.org/10.1590/1676-0611-BN-2019-0815 Abstract: In the present work, we synonymize Micropholis compta under M. gardneriana due to the overlap of morphoanatomical characters and the absence of distinctive attributes, verified during taxonomic and anatomical study of the genus Micropholis for Brazil. This study provides an updated description of M. gardneriana, including macro- and micro-morphological data, a distribution map, and comments on conservation status, ecological and taxonomy. Keywords: Chrysophylloideae, leaf anatomy, Neotropics, South America, taxonomy. Um novo sinônimo para Micropholis gardneriana (Sapotaceae) com descrição completa, anatomia e notas de distribuição Resumo: No presente trabalho, sinonimizamos Micropholis compta sob M. gardneriana devido à sobreposição de caracteres morfoanatômicos e ausência de atributos distintivos, verificado durante estudo taxonômico e anatômico do gênero Micropholis para o Brasil. -
Gambeya Korupensis (Sapotaceae: Chrysophylloideae), a New Rain Forest Tree Species from the Southwest Region in Cameroon
KEW BULLETIN (2016) 71:28 ISSN: 0075-5974 (print) DOI 10.1007/S12225-016-9633-X ISSN: 1874-933X (electronic) Gambeya korupensis (Sapotaceae: Chrysophylloideae), a new rain forest tree species from the Southwest Region in Cameroon Corneille E. N. Ewango1,2, David Kenfack3, Moses Nsanyi Sainge4, Duncan W. Thomas5 & Xander M. van der Burgt6 Summary. Gambeya korupensis Ewango & Kenfack (Sapotaceae: Chrysophylloideae), a new rain forest tree species from the Southwest Region in Cameroon, is described and illustrated. A distribution map is provided. G. korupensis has the leaf blade below pubescent on the midribs and secondary nerves, flowers with a pedicel 0.5 – 1 mm long, and a fruit which is ovoid, attenuate at the apex, 5-ridged, verrucose between the ridges, and bright red at maturity. The conservation status of G. korupensis is assessed as Vulnerable according to IUCN criteria. Key Words. Chrysophyllum, conservation, IUCN Vulnerable, Korup National Park. Introduction 2006; Burgt 2009; Ewango & Breteler 2001; Kenfack Tropical forests inspire botanists and ecologists et al. 2004). The collections were also compared with because of their high diversity and the numerous authoritatively named material of all tropical African species still to be described. Great interest has been species of Gambeya in various herbaria (mostly still aroused by the likely impact of climate change and stored under Chrysophyllum L.; see below). The species fi development on their species diversity and more effort was identi ed as new and provisionally named as Tulestea is needed to document poorly known areas of sp. nov. based on fruit structure by D. W. Thomas biodiversity conservation priority, before their species (Thomas et al. -
Caractéristiques Floristiques De La Zone De Prony À Goro
RAPPORT DE CONSULTANCE CARACTÉRISTIQUES FLORISTIQUES DE LA ZONE DE PRONY À GORO Prilchardiopsis Jeanneneyi Instllut de reeherelTa pour le delleloppemem Laboratoire de Botanique et d'Écologie Appliquée Rapport établi par Tanguy JAFFRÉ (avec la collaboration de F. RIGAULT et G. DAGOSTINI) Juillet 2000 • • • • • • CARACTERISTIQUES FLORISTIQUES DE LA ZONE DE • PRONY A GORO • • • Tanguy JatTré, IRD, Centre de Nouméa. • (Avec la coilaboralion de F. Rigault el de G. Dagoslini) • • • • Méthode de travail Le temps très court imparti pour cette étude, à une période où peu de plantes sont en • fleurs, nous a permis de réaliser seulement un inventaire floristique partiel de la zone d'étude. Aussi avons-nous basé davantage notre analyse sur les récoltes anciennes que sur celles • etTectuées fin mai courant juin, au cours des sorties sur le terrain, réalisées par l'IRD et ia • STRAS. Nous avons également pris en compte les données floristiques laissées par S. McCoy, • lors de ses passages à l'herbier pour identification d'échantillons. Les prospections que nous avons réalisées ont consisté principalement à parcourir • quelques biotopes représentatifs, situés en bordure des pistes principales de la partie centrale de la zone d'étude. Nous nous sommes égaiement rendus dans les parties basses des réserves • botaniques du Pic du Grand Kaori, et du Mt Oungoné, ainsi que dans la zone sur gabbros de la • Baie Nord. Un survol de la zone d'étude en hélicoptère, avec quelques arrêts, nous a permis • d'avoir accès à des secteurs peu connus de Port Boisé et de la Kuébini. Nous avons recherché les informations, dans les 22 volumes de la Flore de la • Nouvelle-Calédonie (Aubréville & al. -
Floristic Relationships of New Caledonian Rainforest Phanerogams
Extract from Telopea 2(6): 631-679 (1986) 63 1 FLORISTIC RELATIONSHIPS OF NEW CALEDONIAN RAINFOREST PHANEROGAMS PH.MORAT!, J.-M. VELLONI& H. S. MACKEE~ (Accepted for publication 16.9.1983) ABSTRACT Morat, Ph.’, Veìllon, J.-M.’ & MacKee, H. S.2 (‘Centre ORSTOM, B.P. A5 Cedex, Nouméa, New Caledonia; 2L3.P. 3349, Nouméa, New Caledonia) 1984. Floristic relatiomhips of New Caledonian rainforest phanerogams. Telopea 2[4): 631-679 - A detailed analysis of the New Caledonian rainforest flora is given; 1499 species in 365 genera and 108 families are listed. Distribution of the species within New Caledonia is given in terms of specificity to rainforest (forestInon-forest and forest occurrence) and to substrate (only ultrabasiclabsent from ultrabasic/present on ultrabasic and other substr: :ss). Distribution of genera is presented according’to occurrences in 12 phyto- geographic units from endemic to pantropical. Sources of information are given. Comparisons with the whole New Caledonian phanerogamic flora are made; 46% of genera and species and 66% of families occur in the rainforest. For the flora the level of specific endemism is c. 75%. Floristic affinities are assessed by: comparison of numbers of genera shared with other regions (pantropical genera included/excluded); and numbers of genera shared exclusively by New Caledonia and 2, 3, 4, 5 or 6 other regions. In these comparisons Australia, New Guinea, Malesia, Fiji, the New Hebrides, the Solomon Islands and then New Zealand have the most genera in common with New Caledonia. A floristic affinity Co-efficient for each territory was calculated from the proportion of the number of common genera to the number of territories in which they occur, for groups of two to six territories. -
Gei Et Al. 2020A
A systematic assessment of the occurrence of trace element hyperaccumulation in the flora of New Caledonia Vidiro Gei1, Sandrine Isnard2,3, Peter D. Erskine1, Guillaume Echevarria1,4, Bruno Fogliani5, Tanguy Jaffré2,3, Antony van der Ent1,4* 1Centre for Mined Land Rehabilitation, Sustainable Minerals Institute, The University of Queensland, St Lucia, QLD 4072, Australia 2botAnique et Modelisation de l’Architecture des Plantes et des végétation (AMAP), Université Montpellier, IRD, CIRAD, CNRS, INRA, Montpellier, France 3botAnique et Modelisation de l’Architecture des Plantes et des végétation (AMAP), IRD, Herbier de Nouvelle-Calédonie, Nouméa, New Caledonia 4Laboratoire Sols et Environnement, Université de Lorraine – INRAE, F54000 Nancy, France 5Équipe ARBOREAL (AgricultuRe BiOdiveRsité Et vALorisation), Institut Agronomique néo-Calédonien (IAC), 98890 Païta, New Caledonia *Corresponding author. E-mail: [email protected] ABSTRACT New Caledonia is a global biodiversity hotspot known for its metal hyperaccumulator plants. X-ray fluorescence technology (XRF) has enabled non-destructive and quantitative determination of elemental concentrations in herbarium specimens from the ultramafic flora of the island. Specimens belonging to six major hyperaccumulator families (Cunoniaceae, Phyllanthaceae, Salicaceae, Sapotaceae, Oncothecaceae and Violaceae) and one to four specimens per species of the remaining ultramafic taxa in the herbarium were measured. XRF scanning included a total of c. 11 200 specimens from 35 orders, 96 families, 281 genera and 1484 species (1620 taxa) and covered 88.5% of the ultramafic flora. The study revealed the existence of 99 nickel hyperaccumulator taxa (65 known previously), 74 manganese hyperaccumulator taxa (11 known previously), eight cobalt hyperaccumulator taxa (two known previously) and four zinc hyperaccumulator taxa (none known previously). -
Biodiversity Conservation and Phylogenetic Systematics Preserving Our Evolutionary Heritage in an Extinction Crisis Topics in Biodiversity and Conservation
Topics in Biodiversity and Conservation Roseli Pellens Philippe Grandcolas Editors Biodiversity Conservation and Phylogenetic Systematics Preserving our evolutionary heritage in an extinction crisis Topics in Biodiversity and Conservation Volume 14 More information about this series at http://www.springer.com/series/7488 Roseli Pellens • Philippe Grandcolas Editors Biodiversity Conservation and Phylogenetic Systematics Preserving our evolutionary heritage in an extinction crisis With the support of Labex BCDIV and ANR BIONEOCAL Editors Roseli Pellens Philippe Grandcolas Institut de Systématique, Evolution, Institut de Systématique, Evolution, Biodiversité, ISYEB – UMR 7205 Biodiversité, ISYEB – UMR 7205 CNRS MNHN UPMC EPHE, CNRS MNHN UPMC EPHE, Muséum National d’Histoire Naturelle Muséum National d’Histoire Naturelle Sorbonne Universités Sorbonne Universités Paris , France Paris , France ISSN 1875-1288 ISSN 1875-1296 (electronic) Topics in Biodiversity and Conservation ISBN 978-3-319-22460-2 ISBN 978-3-319-22461-9 (eBook) DOI 10.1007/978-3-319-22461-9 Library of Congress Control Number: 2015960738 Springer Cham Heidelberg New York Dordrecht London © The Editor(s) (if applicable) and The Author(s) 2016 . The book is published with open access at SpringerLink.com. Chapter 15 was created within the capacity of an US governmental employment. US copyright protection does not apply. Open Access This book is distributed under the terms of the Creative Commons Attribution Noncommercial License, which permits any noncommercial use, distribution, and reproduction in any medium, provided the original author(s) and source are credited. All commercial rights are reserved by the Publisher, whether the whole or part of the material is concerned, specifi cally the rights of translation, reprinting, reuse of illustrations, recitation, broadcasting, reproduction on microfi lms or in any other physical way, and transmission or information storage and retrieval, electronic adaptation, computer software, or by similar or dissimilar methodology now known or hereafter developed. -
David Vela, Superintendent Grand Teton National Park John D
David Vela, Superintendent Grand Teton National Park John D. Rockefeller, Jr. Memorial Parkway Re: Telecommunications Infrastructure Plan EA Dear Mr. Vela & National Park Staff, Environmental Health Trust (EHT) is a nonprofit Think Tank and policy organization dedicated to identifying and reducing environmental health hazards. EHT provides independent scientific research and advice on controllable environmental hazards to local, state and national governments. Today, we write to advise you of scientific grounds for major health and environmental concerns about the proposal for the installation of wireless telecommunications facilities and associated infrastructure at nine developed areas in the park and to express our grave concerns about this planned expansion of mobile communications in Grand Teton National Park. You may recall your discussions last year with me about the need to limit exposures to wildlife and fauna from wireless radiation that took place when we met as part of the City Kids final ascent of the Grand. We fully recognize there is a need for communication for emergency purposes. We further recognize that the Park plays a unique role in our country and in our lives by providing a wilderness that is apart from the normal hectic life that many Americans lead today. We are deeply concerned that by expanding wireless communications this proposal will irrevocably impair the wilderness experience and that there are wired solutions that would be far less damaging. The transmissions to and from these proposed microwave wireless installations will be emissions that are an environmental pollutant known to cause cancer (in both experimental animals and humans) and other adverse health and environmental effects (e.g., on birds, bees, trees) according to internationally recognized authoritative research, including studies conducted by the U.S. -
Van Der Ent Et Al. 2016H
RECENT ADVANCES IN DEVELOPING TROPICAL NICKEL AGROMINING A. van der Ent1,2,, *G. Echevarria2 and P. Erskine1 1Centre for Mined Land Rehabilitation, Sustainable Minerals Institute, The University of Queensland, Australia. 2Université de Lorraine – INRA, Laboratoire Sols et Environnement, UMR 1120, France. (*Corresponding author: [email protected]) ABSTRACT Hyperaccumulator plants can be utilized as ‘metal crops’ in agromining operations. This emerging technology produces ‘bio-ore’ by growing ‘metal crops’ on sub-economic ore materials, such as natural ultramafic soils. In a typical application plant material is periodically harvested, followed by air-drying and incineration to produce the bio-ore intermediate. The bio-ore is of very high grade (>15 wt. % nickel), and of high purity, and may be processed into a number of different products (including nickel metal, nickel- based catalysts and pure nickel salts). Current research efforts from our team focus on Mediterranean climate field trials (Albania, Spain) and tropical climate field trials (Malaysia, Indonesia). Field-scale demonstrations are required to provide evidence of real-life performance and of economic viability. If the trials are successful, agromining may in the near future support local livelihoods with income opportunities as an alternative type of agriculture: to farm nickel. KEYWORDS Agromining, Phytomining, Nickel, Strip-mining, Tropical Ultramafic Soils. INTRODUCTION AND BACKGROUND Hyperaccumulators, plants with the exceptional ability to uptake and concentrate trace elements in their shoots, can be utilized as ‘metal crops’ in agromining operations (Van der Ent et al., 2013a; Chaney et al., 1998; 2007; Baker et al., 2010). Agromining produces ‘bio-ore’ from harvested ‘metal crops’ grown on unconventional resources such as natural ultramafic soils (Van der Ent et al., 2015a). -
Diversity Dynamics in New Caledonia: Towards the End of the Museum Model? Marianne Espeland1,2,3* and Jérôme Murienne3,4
Espeland and Murienne BMC Evolutionary Biology 2011, 11:254 http://www.biomedcentral.com/1471-2148/11/254 RESEARCHARTICLE Open Access Diversity dynamics in New Caledonia: towards the end of the museum model? Marianne Espeland1,2,3* and Jérôme Murienne3,4 Abstract Background: The high diversity of New Caledonia has traditionally been seen as a result of its Gondwanan origin, old age and long isolation under stable climatic conditions (the museum model). Under this scenario, we would expect species diversification to follow a constant rate model. Alternatively, if New Caledonia was completely submerged after its breakup from Gondwana, as geological evidence indicates, we would expect species diversification to show a characteristic slowdown over time according to a diversity-dependent model where species accumulation decreases as space is filled. Results: We reanalyze available datasets for New Caledonia and reconstruct the phylogenies using standardized methodologies; we use two ultrametrization alternatives; and we take into account phylogenetic uncertainty as well as incomplete taxon sampling when conducting diversification rate constancy tests. Our results indicate that for 8 of the 9 available phylogenies, there is significant evidence for a diversification slowdown. For the youngest group under investigation, the apparent lack of evidence of a significant slowdown could be because we are still observing the early phase of a logistic growth (i.e. the clade may be too young to exhibit a change in diversification rates). Conclusions: Our results are consistent with a diversity-dependent model of diversification in New Caledonia. In opposition to the museum model, our results provide additional evidence that original New Caledonian biodiversity was wiped out during the episode of submersion, providing an open and empty space facilitating evolutionary radiations. -
INDEX to GENERA and SPECIES Genera and Species Listed in Appendices Are Not Indexed
INDEX TO GENERA AND SPECIES Genera and species listed in appendices are not indexed Abarema filamentosa . 483 minuta ........................ 444 Abrophyllum . .. 223 Arenga undulatifolia .................. 444 Abryna regispetri .................... 94 Argyrodendron peralatum . 373 Acacia. .. 11 Arhopala buddTia .................... 292 Acalypha stipulacea .................. 327 metamuta ....................... 292 Acantho/epsls ...................... 120 Armigeres ....................... 89, 97 Acanthomyrmex ..................... 120 dolichocephalus . .. 93 Acer saccharum ..................... 219 flavus .. .. 93 Acmena acuminatissima ................ 327 Artocarpus ovatus .................... 328 Acronychia vestita ................... 219 Asyndetus . 185 Acropsilus . 185 Athertonia diversifolia .. .. 224, 225 Acropyga ......................... 120 Atta ............................ 10 Actyolepis puspa .................... 292 Attalea acaulis . 479 Acylophorus ................... 88-91, 93 funifera .................. 477-479, 483 Adinandra ...................... .. 223 humilis ........................ 483 Aedes gombakensis . .. 93 Baccaurea kunst/eri . 155 Aenictus . 120 Bactris . 483 Afromomum ..................... .. 219 Baptista ................. 88-90, 93, 96, 97 Agelaea bomeensis ................... 441 Barbodes collingwoodi .... 309-312, 380, 381, 384 Aglaia ditfusa ...................... 327 Barringtonia . 429 iloilo ......................... 328 Basilia hispida . .. 91 llanosiana ...................... 327 Batraxis . .. 93 longipes