Northern Hemisphere Origin, Transoceanic Dispersal, And

Total Page:16

File Type:pdf, Size:1020Kb

Northern Hemisphere Origin, Transoceanic Dispersal, And Journal of Biogeography (J. Biogeogr.) (2011) 38, 517–530 ORIGINAL Northern Hemisphere origin, transoceanic ARTICLE dispersal, and diversification of Ranunculeae DC. (Ranunculaceae) in the Cenozoic Khatere Emadzade1,2 and Elvira Ho¨randl1* 1Department of Systematic and Evolutionary ABSTRACT Botany, University of Vienna, Rennweg 14, Aim The role of dispersal versus vicariance for plant distribution patterns has 1030 Vienna, Austria, 2Department of Botany, Research Institute of Plant Sciences, Ferdowsi long been disputed. We study the temporal and spatial diversification of University of Mashhad, Mashhad, Iran Ranunculeae, an almost cosmopolitan tribe comprising 19 genera, to understand the processes that have resulted in the present inter-continental disjunctions. Location All continents (except Antarctica). Methods Based on phylogenetic analyses of nuclear and chloroplast DNA sequences for 18 genera and 89 species, we develop a temporal–spatial framework for the reconstruction of the biogeographical history of Ranunculeae. To estimate divergence dates, Bayesian uncorrelated rates analyses and four calibration points derived from geological, fossil and external molecular information were applied. Parsimony-based methods for dispersal–vicariance analysis (diva and Mesquite) and a maximum likelihood-based method (Lagrange) were used for reconstructing ancestral areas. Six areas corresponding to continents were delimited. Results The reconstruction of ancestral areas is congruent in the diva and maximum likelihood-based analyses for most nodes, but Mesquite reveals equivocal results at deep nodes. Our study suggests a Northern Hemisphere origin for the Ranunculeae in the Eocene and a weakly supported vicariance event between North America and Eurasia. The Eurasian clade diversified between the early Oligocene and the late Miocene, with at least three independent migrations to the Southern Hemisphere. The North American clade diversified in the Miocene and dispersed later to Eurasia, South America and Africa. Main conclusions Ranunculeae diversified between the late Eocene and the late Miocene. During this time period, the main oceanic barriers already existed between continents and thus dispersal is the most likely explanation for the current distribution of the tribe. In the Southern Hemisphere, a vicariance model related to the break-up of Gondwana is clearly rejected. Dispersals between continents could have occurred via migration over land bridges, such as the Bering Land Bridge, or via long-distance dispersal. *Correspondence: Elvira Ho¨randl, Department of Systematic and Evolutionary Botany, Keywords University of Vienna, Rennweg 14, 1030 Vienna, Austria. Cenozoic, historical biogeography, long-distance dispersal, molecular dating, E-mail: [email protected] Ranunculeae, transoceanic dispersal, vicariance. (e.g. Wiley, 1998; de Queiroz, 2005; Waters & Craw, 2006). INTRODUCTION Molecular-based phylogenetic studies based on DNA Today it is widely accepted that disjunct distributions can be sequences and estimates of divergence times of lineages explained either by fragmentation of widespread ancestors supported the role of dispersal as a primary process shaping by vicariant (isolating) events or by dispersal across a barrier distribution patterns in both animals and plants (reviewed by ª 2010 Blackwell Publishing Ltd http://wileyonlinelibrary.com/journal/jbi 517 doi:10.1111/j.1365-2699.2010.02404.x K. Emadzade and E. Ho¨ randl de Queiroz, 2005). These studies provide evidence supporting dating by Paun et al. (2005) just one external calibration, a hypothesis of transoceanic dispersal versus vicariance (Giv- namely the time period between the minimum and maximum nish & Renner, 2004; Sanmartı´n & Ronquist, 2004; de Queiroz, age of the split between Ranunculus and Xanthorhiza, was 2005). available. This calibration was based on a dating approach Widespread and species-rich plant families such as the using the angiosperm family tree, which confers some uncer- Ranunculaceae Juss. provide model systems for studying tainty on terminal nodes (Wikstro¨m et al., 2001). The distant biogeographical processes. This family has a crown age of relationship of Xanthorhiza and Ranunculus within Ranuncul- c. 75 Ma (Anderson et al., 2005). The fossil record documents aceae (Wang et al., 2009) is another source of inaccuracy. the considerable differentiation of Ranunculaceae and their Hoffmann et al. (2010) simply derived two calibration points radiation throughout the world during the Neogene in the from Paun et al. (2005). Moreover, previous age estimates for Northern Hemisphere (Ziman & Keener, 1989). Although the tribe suffered from incomplete sampling of genera and the Ziman & Keener (1989) proposed the origin of some tribes lack of internal calibration points. Therefore, the timing of within the ancient floras of eastern Asia (e.g. Anemoneae, biogeographical events has remained tentative. To get a reliable Clematideae) or in North America (e.g. Hydrastideae), they temporal framework for our biogeographical hypotheses, we emphasized that it is difficult to pinpoint the origin of some aimed to refine the divergence times within Ranunculeae by tribes such as the cosmopolitan Ranunculeae. using a new external and three additional internal calibrations, Ranunculeae DC. comprise 19 genera (Emadzade et al., and a more complete sampling of the tribe. 2010) and about 650 species (Tamura, 1995), most of which We combine here the results from molecular dating and are adapted to temperate and cold climates and occur in biogeographical analyses to provide a comprehensive hypoth- mountain regions of the world. Molecular phylogenetic studies esis of the history of Ranunculeae. The aims of this study are within Ranunculaceae suggest that this tribe is monophyletic to: (1) reconstruct divergence dates within Ranunculeae; (2) (Hoot, 1995; Johansson, 1995, 1998; Ro et al., 1997; Lehnebach determine the geographical origin for the tribe; (3) reconstruct et al., 2007; Hoot et al., 2008; Wang et al., 2009). Former the main factor(s) shaping the modern distribution of the molecular phylogenetic studies on Ranunculeae have concen- tribe, including the relative role of long-distance dispersal trated either on certain geographical areas (e.g. New Zealand, (LDD) and vicariance; and (4) identify the main migration Lockhart et al., 2001; the Mediterranean area, Paun et al., routes. 2005; the Southern Hemisphere, Lehnebach, 2008; Africa, Gehrke & Linder, 2009; the Arctic, Hoffmann et al., 2010) or MATERIALS AND METHODS certain genera of the tribe (e.g. Ranunculus,Ho¨randl et al., 2005; Laccopetalum, Lehnebach et al., 2007; Hamadryas, Hoot Taxon sampling et al., 2008). Phylogenetic relationships and taxonomy of genera have been established based on molecular and mor- We sampled 89 taxa, representing 18 of the 19 genera phological data (Emadzade et al., 2010). However, a complete (Emadzade et al., 2010) included in the Ranunculeae. The biogeographical study of all genera of the tribe is still lacking. number of species sampled and the number of species in total The distribution patterns of this tribe provide a model is given for each genus in Fig. 1. Eight genera were sampled system for studying vicariance versus dispersal. Ranunculus is completely; for the others our sampling of species aimed to the only genus distributed on all continents (Fig. 1h). In cover the distribution range of the genus. For the large genus contrast, most other genera in this tribe have very restricted Ranunculus s. str., at least two species were studied from each distributions, and the monotypic genera are endemic to small of the clades and subclades identified in previous studies areas, e.g. Arcteranthis, Beckwithia, Cyrtorhyncha and Kumlie- (Ho¨randl et al., 2005; Paun et al., 2005; Hoffmann et al., nia (North America; Fig. 1a, c, e), Callianthemoides and 2010; Emadzade et al., submitted). Only the monotypic genus Laccopetalum (South America; Fig. 1b, f), Paroxygraphis (Asia; Paroxygraphis, endemic to the Himalayas, was not included Fig. 1g) and Peltocalathos (South Africa; Fig. 1g). Some small because material was not available. For reconstruction of the genera, such as Ceratocephala and Myosurus, are mainly phylogeny of the tribe we used Anemone and Isopyrum as distributed in the Northern Hemisphere (Fig. 1b, f), but some outgroup taxa and 89 species of Ranunculeae for a maximum species occur in the Southern Hemisphere (Tamura, 1995). parsimony analysis of the combined data set as in Emadzade Trautvetteria has a disjunct distribution in eastern Asia and et al. (2010) (see Appendix S1 in Supporting Information). eastern and western North America (Fig. 1h). The species of To improve the external calibration for age estimates (see this genus have been considered as relicts of the Cenozoic below), we used two outgroup taxa from two different (Tertiary) temperate flora (Thorne, 1973). Interestingly, some subgenera of Clematis (Clematis ganpiniana and Clematis of the closely related genera in Ranunculeae, e.g. Callianthe- patens; Wencai & Gilbert, 2001) from Anemoneae, the sister moides, Hamadryas and Peltocalathos, occur on different tribe to Ranunculeae (Wang et al., 2009), and 86 taxa of continents (Fig. 1b, e). Ranunculeae for Bayesian analysis (see below). We included Previous age estimates based on molecular data suggested 68 species of Ranunculus for age estimates because two that the origin of Ranunculeae dates back to the mid Eocene internal calibration points were available within
Recommended publications
  • Electronic Appendix 2B. Phylogenetic Relationships of Ranunculus
    R. oxyspermus R. psilostachys R. rumelicus R. sprunerianus R. argyreus R. damascenus R. macrorrhynchus R. millefolius R. hierosolymitanus R. cicutarius R. garganicus R. millefoliatus R. heterorhizus R. illyricus R. montanus R. aduncus R. apenninus R. pollinensis R. sartorianus R. marschlinsii R. carinthiacus R. venetus R. pseudomontanus R. gouanii R. carpaticus R. villarsii R. afghanicus X I R. aucheri R. elbursensis R. termei R. leptorrhynchus R. linearilobus R. makaluensis R. macropodioides R. papyrocarpus R. regelianus R. paludosus R. pseudomillefoliatus R. olissiponensis R. bullatus R. gregarius R. spicatus R. cortusifolius_Tenerife R. gracilis R. asiaticus R. amblyolobus R. buhsei R. cappadocicus R. breyninus_Alps R. brachylobus R. fascicularis R. hispidus R. septentrionalis R. acriformis R. petiolaris R. hawaiiensis R. mauiensis R. maclovianus R. orthorhynchus R. diffusus R. oreophytus R. rarae R. tenuirostrus R. macounii R. repens R. marginatus R. muricatus R. cornutus R. trilobus R. serpens R. polyanthemos R. sardous R. submarginatus R. bulbosus R. neapolitanus R. multifidus R. pinnatus R. pensylvanicus R. silerifolius R. cantoniensis R. chinensis R. caprarum R. peduncularis R. bonariensis R. brutius R. dissectus R. caucasicus R. sojakii R. arvensis R. arvensis R. acris R. glabriusculus R. japonicus R. lanuginosus R. granatensis R. serbicus R. laetus_1750 R. laetus_1761 R. taisanensis R. grandiflorus R. kotschyi R. velutinus R. baldschuanicus R. cassius R. occidentalis R. uncinatus R. stagnalis R. tembensis R. chius R. parviflorus R. constantinopolitanus R. strigillosus R. sericeus R. pinardi R. cheirophyllus R. ficariifolius R. volkensii R. flagelliformis R. ophioglossifolius R. lateriflorus R. flammula R. reptans R. lingua R. alismifolius R. hydrophilus R. meyeri R. pulchellus R. brotherusii R. pseudopygmaeus R.
    [Show full text]
  • Ranunculus Repens
    TREATMENT OPTIONS from the book Weed Control in Natural Areas in the Western United States This does not constitute a formal recommendation. When using herbicides always read the label, and when in doubt consult your farm advisor or county agent. This is an excerpt from the book Weed Control in Natural Areas in the Western United States and is available wholesale through the UC Weed Research & Information Center (wric.ucdavis.edu) or retail through the Western Society of Weed Science (wsweedscience.org) or the California Invasive Species Council (cal-ipc.org). Ranunculus repens Creeping buttercup Family: Ranunculaceae (buttercup) NON-CHEMICAL CONTROL Cultural: grazing P Cultural: prescribed burning P Mechanical: mowing and cutting P low growing plants will escape injury and quickly recover Mechanical: tillage F─G must be conducted before roots become well established Mechanical: grubbing, digging or hand F creeping roots, only effective on small patches, remove all stem pulling fragments CHEMICAL CONTROL The following specific use information is based on published papers and reports by researchers and land managers. Other trade names may be available, and other compounds also are labeled for this weed. Directions for use may vary between brands; see label before use. 2,4-D E Imazapic NIA Aminocyclopyrachlor + chlorsulfuron E Imazapyr NIA Aminopyralid G─E Metsulfuron E Paraquat NIA Chlorsulfuron E Picloram E Clopyralid NIA Rimsulfuron NIA Dicamba E Sulfometuron NIA Glyphosate E Sulfosulfuron E* Hexazinone NIA Triclopyr G E = Excellent control, generally better than 95% * = Likely based on results of observations of G = Good control, 80-95% related species FLW = flowering F = Fair control, 50-80% NIA = No information available P = Poor control, below 50% Fa = Fall Control includes effects within the season of treatment.
    [Show full text]
  • Myosurus Australis
    Myosurus australis FAMILY : RANUNCULACEAE BOTANICAL NAME : Myosurus australis F.Muell., Trans. Philos. Soc. Victoria 1: 6 (1854) COMMON NAME : Southern mousetail COMMONWEALTH STATUS (EPBC Act): Not Listed TASMANIAN STATUS (TSP Act): endangered Illustration by Richard Hale Description Myosurus australis is a short-lived annual herb with a rosette of rather fleshy narrow- linear leaves. The leaves are up to 10 cm long and have entire margins, and usually wither before fruit develops. Several simple flower stems arise from the base of the plant, each bearing a single flower; the stems are 1 to 3 cm long at flowering, elongating to up to 10 cm in fruit. The flowers are very small and greenish-yellow in colour; there are 5 sepals, each 3 to 5 mm long and with a basal spur, 0 to 5 minute petals and 5 to 10 stamens. The fruit consists of 100 to 300 small fruitlets (achenes) arranged along the top section of the flower stem in a dense slender spike up to 4 cm long. The achenes are dry, leathery and slightly flattened, with a short, erect beak (description from Curtis & Morris 1975, Walsh & Entwisle 1996). Flowering material has been collected in Tasmania in mid November; the species’ flowering period in Victoria is cited as September to November (Walsh & Entwisle 1996). [Myosurus australis was known previously as Myosurus minimus L. sensu Curtis & Morris (1975).] Distribution and Habitat Myosurus australis is endemic to Australia, occurring in all mainland States (Eichler et al. 2007). In Tasmania the species has been recorded at just two sites c. 55 km apart, one in the Southern Midlands and one in the Central Plateau, the altitude at the respective sites being 400 m and 925 m above sea level.
    [Show full text]
  • Outline of Angiosperm Phylogeny
    Outline of angiosperm phylogeny: orders, families, and representative genera with emphasis on Oregon native plants Priscilla Spears December 2013 The following listing gives an introduction to the phylogenetic classification of the flowering plants that has emerged in recent decades, and which is based on nucleic acid sequences as well as morphological and developmental data. This listing emphasizes temperate families of the Northern Hemisphere and is meant as an overview with examples of Oregon native plants. It includes many exotic genera that are grown in Oregon as ornamentals plus other plants of interest worldwide. The genera that are Oregon natives are printed in a blue font. Genera that are exotics are shown in black, however genera in blue may also contain non-native species. Names separated by a slash are alternatives or else the nomenclature is in flux. When several genera have the same common name, the names are separated by commas. The order of the family names is from the linear listing of families in the APG III report. For further information, see the references on the last page. Basal Angiosperms (ANITA grade) Amborellales Amborellaceae, sole family, the earliest branch of flowering plants, a shrub native to New Caledonia – Amborella Nymphaeales Hydatellaceae – aquatics from Australasia, previously classified as a grass Cabombaceae (water shield – Brasenia, fanwort – Cabomba) Nymphaeaceae (water lilies – Nymphaea; pond lilies – Nuphar) Austrobaileyales Schisandraceae (wild sarsaparilla, star vine – Schisandra; Japanese
    [Show full text]
  • Atlas of Rare Endemic Vascular Plants of the Arctic
    Atlas of Rare Endemic Vascular Plants of the Arctic Technical Report No. 3 About CAFF Theprogram for the Conservation of Arctic Flora and Fauna (CAFF) of the Arctic Council was established lo address the special needs of Arctic ecosystems, species and thcir habitats in the rapid ly developing Arctic region. Itwas initiated as one of'four programs of the Arctic Environmental Protcction Strategy (AEPS) which was adopted by Canada, Denmark/Greenland, Finland, lceland, Norway, Russia, Swcdcn and the United States through a Ministeria! Declaration at Rovaniemi, Finland in 1991. Other programs initi­ ated under the AEPS and overlaken hy the Are.tie Council are the ArcticMonitoring and assessment Programme (AMAP), the program for Emergency Prevention, Preparcd­ ness and Response (EPPR) and the program for Protection of the Arctic Marine Envi­ ronment (PAME). Sinceits inaugural mccti.ng in Ottawa, Canada in 1992, the CAFF program has provided scientists, conscrvation managers and groups, and indigenous people of the north with a distinct forum in which lo tackle a wide range of Arctic conservation issues at the cir­ cumpolar level. CAFF's main goals, which are achieved in keeping with the concepts of sustainable developrnertt and utilisation, are: • to conserve Arctic Jlora and fauna, thcir diversity and thcir habitats; • to protect the Arctic ecosystems from threats; • to improve conservation management laws, reg ulations and practices for the Arclic; • to integrale Arctic interests into global conservation fora. CAFF operates rhrough a system of Designated Agencies and National Representatives responsible for CAFF in thcir rcspcctivc countries. CAFF also has an International Work­ ing Group wh.ith has met annually to assess progrcss and to develop Annual WorkPlans.
    [Show full text]
  • Terr–3 Special-Status Plant Populations
    TERR–3 SPECIAL-STATUS PLANT POPULATIONS 1.0 EXECUTIVE SUMMARY During 2001 and 2002, the review of existing information, agency consultation, vegetation community mapping, and focused special-status plant surveys were completed. Based on California Native Plant Society’s (CNPS) Electronic Inventory of Rare and Endangered Vascular Plants of California (CNPS 2001a), CDFG’s Natural Diversity Database (CNDDB; CDFG 2003), USDA-FS Regional Forester’s List of Sensitive Plant and Animal Species for Region 5 (USDA-FS 1998), U.S. Fish and Wildlife Service Species List (USFWS 2003), and Sierra National Forest (SNF) Sensitive Plant List (Clines 2002), there were 100 special-status plant species initially identified as potentially occurring within the Study Area. Known occurrences of these species were mapped. Vegetation communities were evaluated to locate areas that could potentially support special-status plant species. Each community was determined to have the potential to support at least one special-status plant species. During the spring and summer of 2002, special-status plant surveys were conducted. For each special-status plant species or population identified, a CNDDB form was completed, and photographs were taken. The locations were mapped and incorporated into a confidential GIS database. Vascular plant species observed during surveys were recorded. No state or federally listed special-status plant species were identified during special- status plant surveys. Seven special-status plant species, totaling 60 populations, were identified during surveys. There were 22 populations of Mono Hot Springs evening-primrose (Camissonia sierrae ssp. alticola) identified. Two populations are located near Mammoth Pool, one at Bear Forebay, and the rest are in the Florence Lake area.
    [Show full text]
  • Vascular Plants and a Brief History of the Kiowa and Rita Blanca National Grasslands
    United States Department of Agriculture Vascular Plants and a Brief Forest Service Rocky Mountain History of the Kiowa and Rita Research Station General Technical Report Blanca National Grasslands RMRS-GTR-233 December 2009 Donald L. Hazlett, Michael H. Schiebout, and Paulette L. Ford Hazlett, Donald L.; Schiebout, Michael H.; and Ford, Paulette L. 2009. Vascular plants and a brief history of the Kiowa and Rita Blanca National Grasslands. Gen. Tech. Rep. RMRS- GTR-233. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 44 p. Abstract Administered by the USDA Forest Service, the Kiowa and Rita Blanca National Grasslands occupy 230,000 acres of public land extending from northeastern New Mexico into the panhandles of Oklahoma and Texas. A mosaic of topographic features including canyons, plateaus, rolling grasslands and outcrops supports a diverse flora. Eight hundred twenty six (826) species of vascular plant species representing 81 plant families are known to occur on or near these public lands. This report includes a history of the area; ethnobotanical information; an introductory overview of the area including its climate, geology, vegetation, habitats, fauna, and ecological history; and a plant survey and information about the rare, poisonous, and exotic species from the area. A vascular plant checklist of 816 vascular plant taxa in the appendix includes scientific and common names, habitat types, and general distribution data for each species. This list is based on extensive plant collections and available herbarium collections. Authors Donald L. Hazlett is an ethnobotanist, Director of New World Plants and People consulting, and a research associate at the Denver Botanic Gardens, Denver, CO.
    [Show full text]
  • High-Elevation Limits and the Ecology of High-Elevation Vascular Plants: Legacies from Alexander Von Humboldt1
    a Frontiers of Biogeography 2021, 13.3, e53226 Frontiers of Biogeography REVIEW the scientific journal of the International Biogeography Society High-elevation limits and the ecology of high-elevation vascular plants: legacies from Alexander von Humboldt1 H. John B. Birks1,2* 1 Department of Biological Sciences and Bjerknes Centre for Climate Research, University of Bergen, PO Box 7803, Bergen, Norway; 2 Ecological Change Research Centre, University College London, Gower Street, London, WC1 6BT, UK. *Correspondence: H.J.B. Birks, [email protected] 1 This paper is part of an Elevational Gradients and Mountain Biodiversity Special Issue Abstract Highlights Alexander von Humboldt and Aimé Bonpland in their • The known uppermost elevation limits of vascular ‘Essay on the Geography of Plants’ discuss what was plants in 22 regions from northernmost Greenland known in 1807 about the elevational limits of vascular to Antarctica through the European Alps, North plants in the Andes, North America, and the European American Rockies, Andes, East and southern Africa, Alps and suggest what factors might influence these upper and South Island, New Zealand are collated to provide elevational limits. Here, in light of current knowledge a global view of high-elevation limits. and techniques, I consider which species are thought to be the highest vascular plants in twenty mountain • The relationships between potential climatic treeline, areas and two polar regions on Earth. I review how one upper limit of closed vegetation in tropical (Andes, can try to
    [Show full text]
  • Vascular Plant Species with Documented Or Recorded Occurrence in Placer County
    A PPENDIX II Vascular Plant Species with Documented or Reported Occurrence in Placer County APPENDIX II. Vascular Plant Species with Documented or Reported Occurrence in Placer County Family Scientific Name Common Name FERN AND FERN ALLIES Azollaceae Mosquito fern family Azolla filiculoides Pacific mosquito fern Dennstaedtiaceae Bracken family Pteridium aquilinum var.pubescens Bracken fern Dryopteridaceae Wood fern family Athyrium alpestre var. americanum Alpine lady fern Athyrium filix-femina var. cyclosorum Lady fern Cystopteris fragilis Fragile fern Polystichum imbricans ssp. curtum Cliff sword fern Polystichum imbricans ssp. imbricans Imbricate sword fern Polystichum kruckebergii Kruckeberg’s hollyfern Polystichum lonchitis Northern hollyfern Polystichum munitum Sword fern Equisetaceae Horsetail family Equisetum arvense Common horsetail Equisetum hyemale ssp. affine Scouring rush Equisetum laevigatum Smooth horsetail Isoetaceae Quillwort family Isoetes bolanderi Bolander’s quillwort Isoetes howellii Howell’s quillwort Isoetes orcuttii Orcutt’s quillwort Lycopodiaceae Club-moss family Lycopodiella inundata Bog club-moss Marsileaceae Marsilea family Marsilea vestita ssp. vestita Water clover Pilularia americana American pillwort Ophioglossaceae Adder’s-tongue family Botrychium multifidum Leathery grapefern Polypodiaceae Polypody family Polypodium hesperium Western polypody Pteridaceae Brake family Adiantum aleuticum Five-finger maidenhair Adiantum jordanii Common maidenhair fern Aspidotis densa Indian’s dream Cheilanthes cooperae Cooper’s
    [Show full text]
  • Literaturverzeichnis
    Literaturverzeichnis Abaimov, A.P., 2010: Geographical Distribution and Ackerly, D.D., 2009: Evolution, origin and age of Genetics of Siberian Larch Species. In Osawa, A., line ages in the Californian and Mediterranean flo- Zyryanova, O.A., Matsuura, Y., Kajimoto, T. & ras. Journal of Biogeography 36, 1221–1233. Wein, R.W. (eds.), Permafrost Ecosystems. Sibe- Acocks, J.P.H., 1988: Veld Types of South Africa. 3rd rian Larch Forests. Ecological Studies 209, 41–58. Edition. Botanical Research Institute, Pretoria, Abbadie, L., Gignoux, J., Le Roux, X. & Lepage, M. 146 pp. (eds.), 2006: Lamto. Structure, Functioning, and Adam, P., 1990: Saltmarsh Ecology. Cambridge Uni- Dynamics of a Savanna Ecosystem. Ecological Stu- versity Press. Cambridge, 461 pp. dies 179, 415 pp. Adam, P., 1994: Australian Rainforests. Oxford Bio- Abbott, R.J. & Brochmann, C., 2003: History and geography Series No. 6 (Oxford University Press), evolution of the arctic flora: in the footsteps of Eric 308 pp. Hultén. Molecular Ecology 12, 299–313. Adam, P., 1994: Saltmarsh and mangrove. In Groves, Abbott, R.J. & Comes, H.P., 2004: Evolution in the R.H. (ed.), Australian Vegetation. 2nd Edition. Arctic: a phylogeographic analysis of the circu- Cambridge University Press, Melbourne, pp. marctic plant Saxifraga oppositifolia (Purple Saxi- 395–435. frage). New Phytologist 161, 211–224. Adame, M.F., Neil, D., Wright, S.F. & Lovelock, C.E., Abbott, R.J., Chapman, H.M., Crawford, R.M.M. & 2010: Sedimentation within and among mangrove Forbes, D.G., 1995: Molecular diversity and deri- forests along a gradient of geomorphological set- vations of populations of Silene acaulis and Saxi- tings.
    [Show full text]
  • Montana Botany Notes Containing Description of New Species, List of Plants Not Heretofore Recorded from the State, and Notes on Disputed Species, 1910
    University of Montana ScholarWorks at University of Montana University of Montana Bulletin: Biological Series, 1901-1910 Flathead Lake Biological Station 3-1-1910 Montana Botany Notes Containing Description of New Species, List of Plants Not Heretofore Recorded from the State, and Notes on Disputed Species, 1910 University of Montana (Missoula, Mont. : 1893-1913). Biological Station, Flathead Lake Marcus E. Jones Follow this and additional works at: https://scholarworks.umt.edu/umbiologicalseries Let us know how access to this document benefits ou.y Recommended Citation University of Montana (Missoula, Mont. : 1893-1913). Biological Station, Flathead Lake and Jones, Marcus E., "Montana Botany Notes Containing Description of New Species, List of Plants Not Heretofore Recorded from the State, and Notes on Disputed Species, 1910" (1910). University of Montana Bulletin: Biological Series, 1901-1910. 15. https://scholarworks.umt.edu/umbiologicalseries/15 This Book is brought to you for free and open access by the Flathead Lake Biological Station at ScholarWorks at University of Montana. It has been accepted for inclusion in University of Montana Bulletin: Biological Series, 1901-1910 by an authorized administrator of ScholarWorks at University of Montana. For more information, please contact [email protected]. BULLETIN. UNIVERSITY OF MONTANA Number 6 b BIOLOGICAL SERIES No. 15 MONTANA BOTANY NOTES CONTAINING Description of New Species, List of Plants Not Heretofore Recorded From the State, and Notes on Disputed Species, With Five Plates BY MARCUS E. JONES, A. M. Prepared From Material Collected at the University of Montana Biological Station UNIVERSITY OF MONTANA Missoula, Montana, U. S. A. March, 1910 Entered August 24, 1901, at Missonla, Montana, as second class matter, under act of Congress, July 16, 1894 BULLETIN, UNIVERSITY OF MONTANA Number 61 BIOLOGICAL SERIES No.
    [Show full text]
  • Annotated Checklist of the Vascular Plant Flora of Grand Canyon-Parashant National Monument Phase II Report
    Annotated Checklist of the Vascular Plant Flora of Grand Canyon-Parashant National Monument Phase II Report By Dr. Terri Hildebrand Southern Utah University, Cedar City, UT and Dr. Walter Fertig Moenave Botanical Consulting, Kanab, UT Colorado Plateau Cooperative Ecosystems Studies Unit Agreement # H1200-09-0005 1 May 2012 Prepared for Grand Canyon-Parashant National Monument Southern Utah University National Park Service Mojave Network TABLE OF CONTENTS Page # Introduction . 4 Study Area . 6 History and Setting . 6 Geology and Associated Ecoregions . 6 Soils and Climate . 7 Vegetation . 10 Previous Botanical Studies . 11 Methods . 17 Results . 21 Discussion . 28 Conclusions . 32 Acknowledgments . 33 Literature Cited . 34 Figures Figure 1. Location of Grand Canyon-Parashant National Monument in northern Arizona . 5 Figure 2. Ecoregions and 2010-2011 collection sites in Grand Canyon-Parashant National Monument in northern Arizona . 8 Figure 3. Soil types and 2010-2011 collection sites in Grand Canyon-Parashant National Monument in northern Arizona . 9 Figure 4. Increase in the number of plant taxa confirmed as present in Grand Canyon- Parashant National Monument by decade, 1900-2011 . 13 Figure 5. Southern Utah University students enrolled in the 2010 Plant Anatomy and Diversity course that collected during the 30 August 2010 experiential learning event . 18 Figure 6. 2010-2011 collection sites and transportation routes in Grand Canyon-Parashant National Monument in northern Arizona . 22 2 TABLE OF CONTENTS Page # Tables Table 1. Chronology of plant-collecting efforts at Grand Canyon-Parashant National Monument . 14 Table 2. Data fields in the annotated checklist of the flora of Grand Canyon-Parashant National Monument (Appendices A, B, C, and D) .
    [Show full text]