Cypress Savanna (Typic Subtype)
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Natural Heritage Program List of Rare Plant Species of North Carolina 2016
Natural Heritage Program List of Rare Plant Species of North Carolina 2016 Revised February 24, 2017 Compiled by Laura Gadd Robinson, Botanist John T. Finnegan, Information Systems Manager North Carolina Natural Heritage Program N.C. Department of Natural and Cultural Resources Raleigh, NC 27699-1651 www.ncnhp.org C ur Alleghany rit Ashe Northampton Gates C uc Surry am k Stokes P d Rockingham Caswell Person Vance Warren a e P s n Hertford e qu Chowan r Granville q ot ui a Mountains Watauga Halifax m nk an Wilkes Yadkin s Mitchell Avery Forsyth Orange Guilford Franklin Bertie Alamance Durham Nash Yancey Alexander Madison Caldwell Davie Edgecombe Washington Tyrrell Iredell Martin Dare Burke Davidson Wake McDowell Randolph Chatham Wilson Buncombe Catawba Rowan Beaufort Haywood Pitt Swain Hyde Lee Lincoln Greene Rutherford Johnston Graham Henderson Jackson Cabarrus Montgomery Harnett Cleveland Wayne Polk Gaston Stanly Cherokee Macon Transylvania Lenoir Mecklenburg Moore Clay Pamlico Hoke Union d Cumberland Jones Anson on Sampson hm Duplin ic Craven Piedmont R nd tla Onslow Carteret co S Robeson Bladen Pender Sandhills Columbus New Hanover Tidewater Coastal Plain Brunswick THE COUNTIES AND PHYSIOGRAPHIC PROVINCES OF NORTH CAROLINA Natural Heritage Program List of Rare Plant Species of North Carolina 2016 Compiled by Laura Gadd Robinson, Botanist John T. Finnegan, Information Systems Manager North Carolina Natural Heritage Program N.C. Department of Natural and Cultural Resources Raleigh, NC 27699-1651 www.ncnhp.org This list is dynamic and is revised frequently as new data become available. New species are added to the list, and others are dropped from the list as appropriate. -
Improved Conservation Plant Materials Released by NRCS and Cooperators Through December 2014
Natural Resources Conservation Service Improved Conservation Plant Materials Released by Plant Materials Program NRCS and Cooperators through December 2014 Page intentionally left blank. Natural Resources Conservation Service Plant Materials Program Improved Conservation Plant Materials Released by NRCS and Cooperators Through December 2014 Norman A. Berg Plant Materials Center 8791 Beaver Dam Road Building 509, BARC-East Beltsville, Maryland 20705 U.S.A. Phone: (301) 504-8175 prepared by: Julie A. DePue Data Manager/Secretary [email protected] John M. Englert Plant Materials Program Leader [email protected] January 2015 Visit our Website: http://Plant-Materials.nrcs.usda.gov TABLE OF CONTENTS Topics Page Introduction ...........................................................................................................................................................1 Types of Plant Materials Releases ........................................................................................................................2 Sources of Plant Materials ....................................................................................................................................3 NRCS Conservation Plants Released in 2013 and 2014 .......................................................................................4 Complete Listing of Conservation Plants Released through December 2014 ......................................................6 Grasses ......................................................................................................................................................8 -
Tropical Deciduous Forests and Savannas
2/1/17 Tropical Coastal Communities Relationships to other tropical forest systems — specialized swamp forests: Tropical Coastal Forests Mangrove and beach forests § confined to tropical and & subtropical zones at the interface Tropical Deciduous Forests of terrestrial and saltwater Mangrove Forests Mangrove Forests § confined to tropical and subtropical § stilt roots - support ocean tidal zones § water temperature must exceed 75° F or 24° C in warmest month § unique adaptations to harsh Queensland, Australia environment - convergent Rhizophora mangle - red mangrove Moluccas Venezuela 1 2/1/17 Mangrove Forests Mangrove Forests § stilt roots - support § stilt roots - support § pneumatophores - erect roots for § pneumatophores - erect roots for O2 exchange O2 exchange § salt glands - excretion § salt glands - excretion § viviparous seedlings Rhizophora mangle - red mangrove Rhizophora mangle - red mangrove Xylocarpus (Meliaceae) & Rhizophora Mangrove Forests Mangrove Forests § 80 species in 30 genera (20 § 80 species in 30 genera (20 families) families) § 60 species OW& 20 NW § 60 species OW& 20 NW (Rhizophoraceae - red mangrove - Avicennia - black mangrove; inner Avicennia nitida (black mangrove, most common in Neotropics) boundary of red mangrove, better Acanthaceae) drained Rhizophora mangle - red mangrove Xylocarpus (Meliaceae) & Rhizophora 2 2/1/17 Mangrove Forests § 80 species in 30 genera (20 families) § 60 species OW& 20 NW Four mangrove families in one Neotropical mangrove community Avicennia - Rhizophora - Acanthanceae Rhizophoraceae -
Understanding the Causes of Bush Encroachment in Africa: the Key to Effective Management of Savanna Grasslands
Tropical Grasslands – Forrajes Tropicales (2013) Volume 1, 215−219 Understanding the causes of bush encroachment in Africa: The key to effective management of savanna grasslands OLAOTSWE E. KGOSIKOMA1 AND KABO MOGOTSI2 1Department of Agricultural Research, Ministry of Agriculture, Gaborone, Botswana. www.moa.gov.bw 2Department of Agricultural Research, Ministry of Agriculture, Francistown, Botswana. www.moa.gov.bw Keywords: Rangeland degradation, fire, indigenous ecological knowledge, livestock grazing, rainfall variability. Abstract The increase in biomass and abundance of woody plant species, often thorny or unpalatable, coupled with the suppres- sion of herbaceous plant cover, is a widely recognized form of rangeland degradation. Bush encroachment therefore has the potential to compromise rural livelihoods in Africa, as many depend on the natural resource base. The causes of bush encroachment are not without debate, but fire, herbivory, nutrient availability and rainfall patterns have been shown to be the key determinants of savanna vegetation structure and composition. In this paper, these determinants are discussed, with particular reference to arid and semi-arid environments of Africa. To improve our current under- standing of causes of bush encroachment, an integrated approach, involving ecological and indigenous knowledge systems, is proposed. Only through our knowledge of causes of bush encroachment, both direct and indirect, can better livelihood adjustments be made, or control measures and restoration of savanna ecosystem functioning be realized. Resumen Una forma ampliamente reconocida de degradación de pasturas es el incremento de la abundancia de especies de plan- tas leñosas, a menudo espinosas y no palatables, y de su biomasa, conjuntamente con la pérdida de plantas herbáceas. En África, la invasión por arbustos puede comprometer el sistema de vida rural ya que muchas personas dependen de los recursos naturales básicos. -
Grassland Resources and Development of Grassland Agriculture in Temperate China
124 Rangelands 10(3), June 1988 Grassland Resources and Development of Grassland Agriculture in Temperate China Zhu Tinachen Natural temperate grasslands occupy 2.4 million km2 or one-quarter ofthe area of China. They form a broad beltfrom the plains of the northeast to the Tibetan Plateau of the southwest (Fig. 1). The nature and distribution of thegrassland is determined in large part by the influence of the monsoon. In the north- east where the monsoon is well developed, the grassland owes its existenceto dry conditions in the spring. Westward and southwestward wherethe monsooninfluence is weaker, the grasslandsoccupy higherelevations (to as high as 5,000 m) in response to the semiarid and arid regional climate. Similarly, temperate grasslands occur at high elevations in mountains of the desert region in northwestern China, far beyond the continuous grassland belt. Some 4,000 species offlowering plants comprise thevegetation ofthese temper- ate grasslands.About 200 are important forage species. The livestock population in China is about 130 million Fig. I Steppe zone of China cattle units. Most of the livestock are dependent on these 1.Meadow steppe, 2.Typical steppe. 3.Desert steppe. 4. Shrub steppe. 5. Alpine steppe. natural temperategrasslands. GrasslandTypes responding to climate and distributed in the form of a belt. Meadows are not zonal; they are controlled by local envi- Based on the concept of zonal vegetation, the natural ronments.About 80 ofthe area of is occu- of China can be divided into two percent grassland temperategrasslands major pied by zone steppetypes and about 20 percent by meadow types: steppe and meadow. -
Sistema De Clasificación Artificial De Las Magnoliatas Sinántropas De Cuba
Sistema de clasificación artificial de las magnoliatas sinántropas de Cuba. Pedro Pablo Herrera Oliver Tesis doctoral de la Univerisdad de Alicante. Tesi doctoral de la Universitat d'Alacant. 2007 Sistema de clasificación artificial de las magnoliatas sinántropas de Cuba. Pedro Pablo Herrera Oliver PROGRAMA DE DOCTORADO COOPERADO DESARROLLO SOSTENIBLE: MANEJOS FORESTAL Y TURÍSTICO UNIVERSIDAD DE ALICANTE, ESPAÑA UNIVERSIDAD DE PINAR DEL RÍO, CUBA TESIS EN OPCIÓN AL GRADO CIENTÍFICO DE DOCTOR EN CIENCIAS SISTEMA DE CLASIFICACIÓN ARTIFICIAL DE LAS MAGNOLIATAS SINÁNTROPAS DE CUBA Pedro- Pabfc He.r retira Qltver CUBA 2006 Tesis doctoral de la Univerisdad de Alicante. Tesi doctoral de la Universitat d'Alacant. 2007 Sistema de clasificación artificial de las magnoliatas sinántropas de Cuba. Pedro Pablo Herrera Oliver PROGRAMA DE DOCTORADO COOPERADO DESARROLLO SOSTENIBLE: MANEJOS FORESTAL Y TURÍSTICO UNIVERSIDAD DE ALICANTE, ESPAÑA Y UNIVERSIDAD DE PINAR DEL RÍO, CUBA TESIS EN OPCIÓN AL GRADO CIENTÍFICO DE DOCTOR EN CIENCIAS SISTEMA DE CLASIFICACIÓN ARTIFICIAL DE LAS MAGNOLIATAS SINÁNTROPAS DE CUBA ASPIRANTE: Lie. Pedro Pablo Herrera Oliver Investigador Auxiliar Centro Nacional de Biodiversidad Instituto de Ecología y Sistemática Ministerio de Ciencias, Tecnología y Medio Ambiente DIRECTORES: CUBA Dra. Nancy Esther Ricardo Ñapóles Investigador Titular Centro Nacional de Biodiversidad Instituto de Ecología y Sistemática Ministerio de Ciencias, Tecnología y Medio Ambiente ESPAÑA Dr. Andreu Bonet Jornet Piiofesjar Titular Departamento de EGdfegfe Universidad! dte Mearte CUBA 2006 Tesis doctoral de la Univerisdad de Alicante. Tesi doctoral de la Universitat d'Alacant. 2007 Sistema de clasificación artificial de las magnoliatas sinántropas de Cuba. Pedro Pablo Herrera Oliver I. INTRODUCCIÓN 1 II. ANTECEDENTES 6 2.1 Historia de los esquemas de clasificación de las especies sinántropas (1903-2005) 6 2.2 Historia del conocimiento de las plantas sinantrópicas en Cuba 14 III. -
Mid-Atlantic Native Meadows Guidelines for Planning, Preparation, Design, Installation, and Maintenance
Mid-Atlantic Native Meadows Guidelines for Planning, Preparation, Design, Installation, and Maintenance Alice Sturm, Mahan Rykiel Associates Stephanie Frischie, Xerces Society for Invertebrate Conservation Mid-Atlantic Native Meadows Guidelines for Planning, Preparation, Design, Installation, and Maintenance Alice Sturm, Mahan Rykiel Associates Stephanie Frischie, Xerces Society for Invertebrate Conservation The Xerces Society is a nonprofit organization that protects the natural world by conserving invertebrates and their habitat. Established in 1971, the Society is a trusted source for science-based information and advice and plays a leading role in promoting the conservation of pollinators and many other invertebrates. We collaborate with people and institutions at all levels and our work to protect bees, butterflies, and other pollinators encompasses all landscapes. Our team draws together experts from the fields of habitat restoration, entomology, plant ecology, education, farming, and conservation biology with a single passion: Protecting the life that sustains us. The Xerces Society for Invertebrate Conservation 628 NE Broadway, Suite 200, Portland, OR 97232 Tel (855) 232-6639 Fax (503) 233-6794 www.xerces.org Regional offices from coast to coast The Xerces Society is an equal opportunity employer and provider. Xerces® is a trademark registered in the U.S. Patent and Trademark Office Founded in 1983, Mahan Rykiel Associates is a 35-person landscape architecture, urban design, and planning firm located in Baltimore, Maryland. The firm works across scales to imagine and realize projects that enrich the human condition and support vibrant natural systems. Research and discovery guide project development that includes public parks, civic plazas, state infrastructure, mixed-use housing, private residences, healthcare facilities, hotels, and commercial centers. -
State of New York City's Plants 2018
STATE OF NEW YORK CITY’S PLANTS 2018 Daniel Atha & Brian Boom © 2018 The New York Botanical Garden All rights reserved ISBN 978-0-89327-955-4 Center for Conservation Strategy The New York Botanical Garden 2900 Southern Boulevard Bronx, NY 10458 All photos NYBG staff Citation: Atha, D. and B. Boom. 2018. State of New York City’s Plants 2018. Center for Conservation Strategy. The New York Botanical Garden, Bronx, NY. 132 pp. STATE OF NEW YORK CITY’S PLANTS 2018 4 EXECUTIVE SUMMARY 6 INTRODUCTION 10 DOCUMENTING THE CITY’S PLANTS 10 The Flora of New York City 11 Rare Species 14 Focus on Specific Area 16 Botanical Spectacle: Summer Snow 18 CITIZEN SCIENCE 20 THREATS TO THE CITY’S PLANTS 24 NEW YORK STATE PROHIBITED AND REGULATED INVASIVE SPECIES FOUND IN NEW YORK CITY 26 LOOKING AHEAD 27 CONTRIBUTORS AND ACKNOWLEGMENTS 30 LITERATURE CITED 31 APPENDIX Checklist of the Spontaneous Vascular Plants of New York City 32 Ferns and Fern Allies 35 Gymnosperms 36 Nymphaeales and Magnoliids 37 Monocots 67 Dicots 3 EXECUTIVE SUMMARY This report, State of New York City’s Plants 2018, is the first rankings of rare, threatened, endangered, and extinct species of what is envisioned by the Center for Conservation Strategy known from New York City, and based on this compilation of The New York Botanical Garden as annual updates thirteen percent of the City’s flora is imperiled or extinct in New summarizing the status of the spontaneous plant species of the York City. five boroughs of New York City. This year’s report deals with the City’s vascular plants (ferns and fern allies, gymnosperms, We have begun the process of assessing conservation status and flowering plants), but in the future it is planned to phase in at the local level for all species. -
The 1700 Native Plants of Bucks County, PA
The 1700 Native Plants of Bucks County, PA Bucks County, PA is blessed with an enormous range of physiographic regions, soil types, and hydrological conditions. Habitats range from the diabase areas of the Upper Bucks to the coastal plains of Lower Bucks, high palisades of the Delaware River to bog remnants, pristine freshwater ponds to tidal areas. These varied conditions host a dizzying array of species, sub‐species, and naturally‐occurring varieties. Common species are regularly available from ArcheWild; many can be grown under contract. Call ArcheWild at 855‐752‐6862 or e‐mail us for more information at: [email protected] Symbol Scientific Name Common Name ACGR2 Acalypha gracilens slender threeseed mercury ACRH Acalypha rhomboidea common threeseed mercury ACVI Acalypha virginica Virginia threeseed mercury ACNE2 Acer negundo boxelder ACNEN Acer negundo var. negundo boxelder ACPE Acer pensylvanicum striped maple ACRU Acer rubrum red maple ACRUR Acer rubrum var. rubrum red maple ACRUT Acer rubrum var. trilobum red maple ACSA2 Acer saccharinum silver maple ACSA3 Acer saccharum sugar maple ACSAS Acer saccharum var. saccharum sugar maple ACSP2 Acer spicatum mountain maple ACMI2 Achillea millefolium common yarrow ACPA Actaea pachypoda white baneberry ACRA7 Actaea racemosa black baneberry ACRAR Actaea racemosa var. racemosa black bugbane ADPE Adiantum pedatum northern maidenhair ADFU Adlumia fungosa allegheny vine AEFL Aesculus flava yellow buckeye AGAU3 Agalinis auriculata earleaf false foxglove AGPU5 Agalinis purpurea purple false foxglove -
Weed Control in Florida Ponds1
Archival copy: for current recommendations see http://edis.ifas.ufl.edu or your local extension office. CIR 707 Weed Control in Florida Ponds1 D.D. Thayer, K. A. Langeland, W.T. Haller, and J.C. Joyce2 Ponds are often built to supplement farm income Site Selection via fish production, for personal enjoyment, or for stormwater management. Soon after the pond is Where you dig a pond can be an important constructed, unforeseen problems often arise. One decision when it comes to preventive control. Proper major problem that occurs is that the pond becomes location can help minimize erosion and nutrient clogged with aquatic plants. The level at which an enrichment from the runoff of silt and inorganic and aquatic plant becomes a weed problem depends on organic fertilizers that decrease the lifespan of the the pond's intended use. A farm pond used primarily pond and limit its usefulness. for weekend fishing can tolerate considerably more Whether you fertilize your pond for fish vegetation than a pond constructed specifically for production or avoid intentional nutrient enrichment, fish production and/or irrigation. Shoreline grasses sites near fertilized fields, feedlots, barnyards, septic can help stabilize and prevent bank erosion, but out of tanks, gardens, roadways, or other sources of runoff control grasses may encroach into the water, where should be avoided. Agricultural and domestic runoff they restrict access and usability. This circular such as from parking lots and roadways may also provides information on aquatic weed identification contribute heavy metals, oils, and pesticide and control for farm and aquaculture ponds. contaminants. If an “ideal” pond location cannot be Prevention is the best technique for reducing found, a berm to divert runoff away from the pond takeover by aquatic weeds. -
Eupatorium Leucolepis (DC.) T
New England Plant Conservation Program Eupatorium leucolepis (DC.) T. & G. var. novae-angliae Fern. New England Boneset Conservation and Research Plan for New England Prepared by: Ted Elliman Ecological Consultant Slingerlands, New York For: New England Wild Flower Society 180 Hemenway Road Framingham, MA 01701 508/877-7630 e-mail: [email protected] • website: www.newfs.org Through a cooperative agreement with Massachusetts Natural Heritage and Endangered Species Program and Manomet, Inc. Approved, Regional Advisory Council, December 2001 1 SUMMARY Eupatorium leucolepis (DC.) T. & G. var. novae-angliae Fern., New England boneset (Asteraceae), is endemic to the coastal plain region of southeastern Massachusetts and southern Rhode Island. New England boneset is classified as a Regionally Rare taxon (Division 2) in Flora Conservanda. The taxon has 16 current occurrences, ten of which are in Massachusetts and six in Rhode Island. Two Massachusetts populations documented in the early twentieth century have been extirpated. The ten existing Massachusetts populations are located in Plymouth County (nine occurrences) and in Barnstable County (one occurrence). The Rhode Island populations are located in Washington County (five occurrences) and in Newport County (one occurrence). New England boneset flowers lack pollen and are male-sterile. Plants reproduce vegetatively from stolons and through the asexual production of viable seeds and embryos in a process known as agamospermy ("without gametes"). In spite of the absence of pollen, a variety of insects visit the flowers, which are in peak bloom in August. New England boneset fruits are dispersed by wind in the fall. The habitat for all of the New England boneset occurrences except for one Rhode Island site is sandy coastal plain pond shores. -
Wildflower Meadows
Online edition: ISSN 2009-6852 National Biodiversity Data Series No. 13. Print edition: ISSN 2009-6844 How-to-guide Creation and management of a wildfl ower meadow All-Ireland Pollinator Plan e I m 2015-2020 r t p n l e e m C a e t n a t a D t i y o t i n s c r o e o iv rd d i io n B at l ed na by tio th Na e www.biodiversityireland.ie/pollinator-plan How-to-guide 4 “How can I create a What is a wildflower wildflower meadow for meadow? A wildfower meadow is many things to many pollinators?” people. To some, a wildfower meadow is a brightly This is the Pollinator Plan’s most frequently asked coloured feld made up of annual species such as question. If we want to ensure our pollinators poppies and cornfowers (left photo, below). These are there when we need them, providing enough were the “weeds” of cereals such as barley. With food (fowers) is key. Planting a native wildfower selective herbicides and improved seed cleaning meadow can help, but creating a sustainable, practices these species have declined. pollinator friendly meadow is more complex than most people realise. That is why the experts at Other people have in mind the traditional Irish EcoSeeds have collaborated with the Pollinator hay meadow (right photo, below). In the last 50 Plan to help produce this How-to-Guide. It will help years the practice of hay making has declined you plan for and carry out your wildfower project.