Ups14 Southern Dry Savanna Factsheet
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Native Plants of East Central Illinois and Their Preferred Locations”
OCTOBER 2007 Native Plants at the University of Illinois at Urbana-Champaign Campus: A Sourcebook for Landscape Architects and Contractors James Wescoat and Florrie Wescoat with Yung-Ching Lin Champaign, IL October 2007 Based on “Native Plants of East Central Illinois and their Preferred Locations” An Inventory Prepared by Dr. John Taft, Illinois Natural History Survey, for the UIUC Sustainable Campus Landscape Subcommittee - 1- 1. Native Plants and Plantings on the UIUC Campus This sourcebook was compiled for landscape architects working on projects at the University of Illinois at Urbana-Champaign campus and the greater headwaters area of east central Illinois.1 It is written as a document that can be distributed to persons who may be unfamiliar with the local flora and vegetation, but its detailed species lists and hotlinks should be useful for seasoned Illinois campus designers as well. Landscape architects increasingly seek to incorporate native plants and plantings in campus designs, along with plantings that include adapted and acclimatized species from other regions. The term “native plants” raises a host of fascinating scientific, aesthetic, and practical questions. What plants are native to East Central Illinois? What habitats do they occupy? What communities do they form? What are their ecological relationships, aesthetic characteristics, and practical limitations? As university campuses begin to incorporate increasing numbers of native species and areas of native planting, these questions will become increasingly important. We offer preliminary answers to these questions, and a suite of electronic linkages to databases that provide a wealth of information for addressing more detailed issues. We begin with a brief introduction to the importance of native plants in the campus environment, and the challenges of using them effectively, followed by a description of the database, online resources, and references included below. -
Botanical Survey of Bussey Brook Meadow Jamaica Plain, Massachusetts
Botanical Survey of Bussey Brook Meadow Jamaica Plain, Massachusetts Botanical Survey of Bussey Brook Meadow Jamaica Plain, Massachusetts New England Wildflower Society 180 Hemenway Road Framingham, MA 01701 508-877-7630 www.newfs.org Report by Joy VanDervort-Sneed, Atkinson Conservation Fellow and Ailene Kane, Plant Conservation Volunteer Coordinator Prepared for the Arboretum Park Conservancy Funded by the Arnold Arboretum Committee 2 Conducted 2005 TABLE OF CONTENTS INTRODUCTION........................................................................................................................4 METHODS....................................................................................................................................6 RESULTS .......................................................................................................................................8 Plant Species ........................................................................................................................8 Natural Communities...........................................................................................................9 DISCUSSION .............................................................................................................................15 Recommendations for Management ..................................................................................15 Recommendations for Education and Interpretation .........................................................17 Acknowledgments..............................................................................................................19 -
Appendix L: Oak Savanna Definition
Appendix L: Oak Savanna Definition Appendix L: Oak Savanna Definition Working Definition of “Savanna” for shaded environments under trees, shifting as the tree canopy becomes more open or closed. Herba- Restoration Efforts at Crane Meadows ceous species typical of prairie and forest co-occur; NWR in addition to a set of very specific savanna species (see lists below) that have high fidelity to this com- General Definition of Southern Dry Savanna: munity type (Texler Personal commun., Drobney Personal commun. (Buchanan 1996). This spatial Savanna habitat at Crane Meadows NWR, like variation within the understory is a function of the savanna across its range, is a fire-dependent, varying degrees of species tolerance to shade and dynamic community characterized by scattered sun. Forbs are an essential component of the under trees or groves of trees, mostly comprised of oaks - story. Another important component of savanna (Quercus sp.) with a canopy cover ranging from 10– 70%, but more typically between 25-50%; and a understory is the shrub layer. The understory of basal area (BA) of 5-50 sq ft / acre. A wide range is savanna on the Anoka Sandplain, including those at Crane Meadows NWR, can be present with or with- used because canopy cover is not the most impor- tant characteristic that defines savanna and also out shrubs. The extent of shrub density is depen- because savanna ecosystems are dynamic and are dent on the subtype savanna classification and the frequency of fire (Law et al. 1994, Swanson 2008, associated with a natural range of variation through space and time. -
Key Points for Sustainable Management of Northern Great Plains Grasslands
CORE Metadata, citation and similar papers at core.ac.uk Provided by Public Research Access Institutional Repository and Information Exchange South Dakota State University Open PRAIRIE: Open Public Research Access Institutional Repository and Information Exchange Natural Resource Management Faculty Publications Department of Natural Resource Management 2019 Looking to the Future: Key Points for Sustainable Management of Northern Great Plains Grasslands Lora B. Perkins Marissa Ahlering Diane L. Larson Follow this and additional works at: https://openprairie.sdstate.edu/nrm_pubs Part of the Ecology and Evolutionary Biology Commons, and the Environmental Sciences Commons REVIEW ARTICLE Looking to the future: key points for sustainable management of northern Great Plains grasslands Lora B. Perkins1,2 , Marissa Ahlering3, Diane L. Larson4 The grasslands of the northern Great Plains (NGP) region of North America are considered endangered ecosystems and priority conservation areas yet have great ecological and economic importance. Grasslands in the NGP are no longer self-regulating adaptive systems. The challenges to these grasslands are widespread and serious (e.g. climate change, invasive species, fragmentation, altered disturbance regimes, and anthropogenic chemical loads). Because the challenges facing the region are dynamic, complex, and persistent, a paradigm shift in how we approach restoration and management of the grasslands in the NGP is imperative. The goal of this article is to highlight four key points for land managers and restoration practitioners to consider when planning management or restoration actions. First, we discuss the appropriateness of using historical fidelity as a restoration or management target because of changing climate, widespread pervasiveness of invasive species, the high level of fragmentation, and altered disturbance regimes. -
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. -
Grass Varieties for North Dakota
R-794 (Revised) Grass Varieties For North Dakota Kevin K. Sedivec Extension Rangeland Management Specialist, NDSU, Fargo Dwight A. Tober Plant Materials Specialist, USDA-NRCS, Bismarck Wayne L. Duckwitz Plant Materials Center Manager, USDA-NRCS, Bismarck John R. Hendrickson Research Rangeland Management Specialist, USDA-ARS, Mandan North Dakota State University Fargo, North Dakota June 2011 election of the appropriate species and variety is an important step in making a grass seeding successful. Grass species and varieties differ in growth habit, productivity, forage quality, drought resistance, tolerance Sto grazing, winter hardiness, seedling vigor, salinity tolerance and many other characteristics. Therefore, selection should be based on the climate, soils, intended use and the planned management. Planting a well-adapted selection also can provide long-term benefi ts and affect future productivity of the stand. This publication is designed to assist North Dakota producers and land managers in selecting perennial grass species and varieties for rangeland and pasture seeding and conservation planting. Each species is described following a list of recommended varieties Contents (releases). Variety origin and the date released are Introduction. 2 included for additional reference. Introduced Grasses . 3 A Plant Species Guide for Special Conditions, found Bromegrass . 3 near the end of this publication, is provided to assist Fescue . 4 in selection of grass species for droughty soils, arid Orchardgrass . 4 Foxtail. 5 or wet environments, saline or alkaline areas and Wheatgrass . 5 landscape/ornamental plantings. Several factors should Timothy. 7 be considered before selecting plant species. These Wildrye . 7 include 1) a soil test, 2) herbicides previously used, Native Grasses . -
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. -
Black Oak Savanna Nature Centres 5 Summer Camp Sign-Up 6 by Kevin Tupman Oak Savanna
THE GRAND STRATEGY NEWSLETTER Volume 15, Number 3 - May-June 2010 Grand River The Grand: Conservation A Canadian Authority Heritage River Feature Fire restores a rare savanna forest 1 Milestones Byng island’s 50th 2 Look Who’s Taking Action Caring for bluebirds 3 Swallow habitat 4 Rotary forest 5 Fire restores a rare forest: What’s happening New programs at black oak savanna nature centres 5 Summer camp sign-up 6 By Kevin Tupman oak savanna. Older oaks now existing within the SWP update 6 Natural Heritage Specialist area are a testament to the vision, progressive for Grand River a grand its time, expressed in the master plan. place to paddle 7 ost people know that some plants and ani- Fire is necessary because this rare ecosystem Water festival photo 7 Mmals are at risk, such as the bald eagle and is sustained by fire. Historically, fire resulted American ginseng, but not many people realize from either lightning or aboriginal inhabitants. Now Available that communities such as forests, can also be at Fire ensures that savanna areas do not turn into Grand new risk. dense forests. Only trees with a high tolerance fishing book 7 It is true that sugar maple woodlots and pine for fire, such as the black oak, are able to sur- plantations are commonplace. However, the vive. European settlers cleared much of the savanna Calendar 8 GRCA is restoring one of the rarest of forests — for agriculture. They also suppressed the fires. a black oak savanna close to Apps’ Mill in Brant This meant that surviving pockets of savanna Cover photo County. -
C10 Beano2.Gen-Wis
LEGUMINOSAE PART DEUX Papilionoideae, Genista to Wisteria Revised May the 4th 2015 BEAN FAMILY 2 Pediomelum PAPILIONACEAE cont. Genista Petalostemum Glycine Pisum Glycyrrhiza Psoralea Hylodesmum Psoralidium Lathyrus Robinia Lespedeza Securigera Lotus Strophostyles Lupinus Tephrosia Medicago Thermopsis Melilotus Trifolium Onobrychis Vicia Orbexilum Wisteria Oxytropis Copyrighted Draft GENISTA Linnaeus DYER’S GREENWEED Fabaceae Genista Genis'ta (jen-IS-ta or gen-IS-ta) from a Latin name, the Plantagenet kings & queens of England took their name, planta genesta, from story of William the Conqueror, as setting sail for England, plucked a plant holding tenaciously to a rock on the shore, stuck it in his helmet as symbol to hold fast in risky undertaking; from Latin genista (genesta) -ae f, the plant broom. Alternately from Celtic gen, or French genet, a small shrub (w73). A genus of 80-90 spp of small trees, shrubs, & herbs native of Eurasia. Genista tinctoria Linnaeus 1753 DYER’S GREENWEED, aka DYER’S BROOM, WOADWAXEN, WOODWAXEN, (tinctorius -a -um tinctor'ius (tink-TORE-ee-us or tink-TO-ree-us) New Latin, of or pertaining to dyes or able to dye, used in dyes or in dyeing, from Latin tingo, tingere, tinxi, tinctus, to wet, to soak in color; to dye, & -orius, capability, functionality, or resulting action, as in tincture; alternately Latin tinctōrius used by Pliny, from tinctōrem, dyer; at times, referring to a plant that exudes some kind of stain when broken.) An escaped shrub introduced from Europe. Shrubby, from long, woody roots. The whole plant dyes yellow, & when mixed with Woad, green. Blooms August. Now, where did I put that woad? Sow at 18-22ºC (64-71ºF) for 2-4 wks, move to -4 to +4ºC (34-39ºF) for 4-6 wks, move to 5-12ºC (41- 53ºF) for germination (tchn). -
Conservation Assessment of Greater Sage-Grouse and Sagebrush Habitats
Conservation Assessment of Greater Sage-grouse and Sagebrush Habitats J. W. Connelly S. T. Knick M. A. Schroeder S. J. Stiver Western Association of Fish and Wildlife Agencies June 2004 CONSERVATION ASSESSMENT OF GREATER SAGE-GROUSE and SAGEBRUSH HABITATS John W. Connelly Idaho Department Fish and Game 83 W 215 N Blackfoot, ID 83221 [email protected] Steven T. Knick USGS Forest & Rangeland Ecosystem Science Center Snake River Field Station 970 Lusk St. Boise, ID 83706 [email protected] Michael A. Schroeder Washington Department of Fish and Wildlife P.O. Box 1077 Bridgeport, WA 98813 [email protected] San J. Stiver Wildlife Coordinator, National Sage-Grouse Conservation Framework Planning Team 2184 Richard St. Prescott, AZ 86301 [email protected] This report should be cited as: Connelly, J. W., S. T. Knick, M. A. Schroeder, and S. J. Stiver. 2004. Conservation Assessment of Greater Sage-grouse and Sagebrush Habitats. Western Association of Fish and Wildlife Agencies. Unpublished Report. Cheyenne, Wyoming. Cover photo credit, Kim Toulouse i Conservation Assessment of Greater Sage-grouse and Sagebrush Habitats Connelly et al. Author Biographies John W. Connelly Jack has been employed as a Principal Wildlife Research Biologist with the Idaho Department of Fish and Game for the last 20 years. He received his B.S. degree from the University of Idaho and M.S. and Ph.D. degrees from Washington State University. Jack is a Certified Wildlife Biologist and works on grouse conservation issues at national and international scales. He is a member of the Western Sage and Columbian Sharp-tailed Technical Committee and the Grouse Specialists’ Group. -
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.