Pocket Guide to Sagebrush
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2012 Planting Lines
San Clemente Island Native Habitat Restoration Program Native Seed Collection, Propagation and Outplanting in Support of San Clemente Island Endangered Species Programs Under Contract With: Naval Facilities Engineering Command Southwest San Diego, California N68711 -05-D-3605-0077 Prepared By: Emily Howe, Korie Merrill, Thomas A. Zink. Soil Ecology and Restoration Group San Diego State University Research Foundation, San Diego, CA Prepared for: Natural Resources Office Environmental Department, Commander, Navy region Southwest, San Diego, CA Table Of Contents Table Of Contents ................................................................................................................ 2 Table of Figures ................................................................................................................... 2 Introduction ......................................................................................................................... 4 1.0 Native Plant Nursery ..................................................................................................... 4 1.1 Nursery Inventory .......................................................................................................... 4 1.2 Seed propagation ........................................................................................................... 5 2.0 Rainfall Data Collection ................................................................................................ 6 3.0 Seed Collection ............................................................................................................. -
"National List of Vascular Plant Species That Occur in Wetlands: 1996 National Summary."
Intro 1996 National List of Vascular Plant Species That Occur in Wetlands The Fish and Wildlife Service has prepared a National List of Vascular Plant Species That Occur in Wetlands: 1996 National Summary (1996 National List). The 1996 National List is a draft revision of the National List of Plant Species That Occur in Wetlands: 1988 National Summary (Reed 1988) (1988 National List). The 1996 National List is provided to encourage additional public review and comments on the draft regional wetland indicator assignments. The 1996 National List reflects a significant amount of new information that has become available since 1988 on the wetland affinity of vascular plants. This new information has resulted from the extensive use of the 1988 National List in the field by individuals involved in wetland and other resource inventories, wetland identification and delineation, and wetland research. Interim Regional Interagency Review Panel (Regional Panel) changes in indicator status as well as additions and deletions to the 1988 National List were documented in Regional supplements. The National List was originally developed as an appendix to the Classification of Wetlands and Deepwater Habitats of the United States (Cowardin et al.1979) to aid in the consistent application of this classification system for wetlands in the field.. The 1996 National List also was developed to aid in determining the presence of hydrophytic vegetation in the Clean Water Act Section 404 wetland regulatory program and in the implementation of the swampbuster provisions of the Food Security Act. While not required by law or regulation, the Fish and Wildlife Service is making the 1996 National List available for review and comment. -
31295015064529.Pdf (3.477Mb)
POPULATION DYNAMICS, REPRODUCTION, AND ACTIVITIES OF THE KANGAROO RAT, DIPODOMYS ORDII, IN WESTERN TEXAS by HERSCHEL VJHITAKER GARNER, B.S., M.S. A DISSERTATION IN ZOOLOGY Submitted to the Graduate Faculty of Texas Tech University in Partial Fulfillment of the Requirements for the Degree of DOCTOR OF PHILOSOPHY Approved Accepted August, 1970 ACKNOWL EDGMENTS I am especially grateful to Professor Robert L. Packard for advising in research methods, aiding in collecting data, and critically reading the manuscript. Additional appreciated suggestions were made by Professors Archie C. Allen, John S. Mecham, Robert W.. Mitchell, Paul V. Prior (now at the University of Nebraska- Omaha), and Chester M. Rowell. Mr. Robert B. Wadley pro vided useful help in developing computer programs used in sorting and analysis of the data. An honorarium from the Department of Biology defrayed some of the cost of travel to the field. My wife, Anita, aided in making collections and recording data. Additional thanks are extended to fellow graduate students who provided help and ideas.' 11 TABLE OF CONTENTS ACKNOWLEDGMENTS ii LIST OF TABLES ; . iv LIST OF ILLUSTRATIONS V I. INTRODUCTION 1 II. METHODS AND MATERIALS 3 III. REPRODUCTION 15 IV. ACTIVITIES 35 V. POPULATION DYNAMICS 43 VI. SUMlvlARY AND CONCLUSIONS 72 LITERATURE CITED 76 111 LIST OF TABLES Table Page 1. Estimation of number of D. ordii on the Kermit area 51 IV LIST OF ILLUSTRATIONS Figure Page 1. The intensive study area viewed from the southern periphery June, 1956 .... 5 2. Diagram of study area showing position of activity center values of animals used in the experimental activity studies 12 3. -
Final Report: Lesser Prairie-Chicken Survey − Kiowa and Rita Blanca National Grasslands, 2014
Final Report: Lesser Prairie-Chicken Survey − Kiowa and Rita Blanca National Grasslands, 2014 Project Manager: Angela Dwyer, Rocky Mountain Bird Observatory, 230 Cherry St., Fort Collins, CO 80521 ([email protected]) Project Director: David Hanni, Rocky Mountain Bird Observatory, 230 Cherry St., Fort Collins, CO 80521 ([email protected]) Introduction The Lesser Prairie-Chicken (Tympanuchus pallidicinctus) (LEPC) occupies grassland habitat consisting of sand sagebrush (Artemisia filifolia), sand shinnery oak (Quercus havardii) and mixed grass vegetation communities of the southern Great Plains. Since the 19th century, LEPC and the habitat upon which they depend has diminished across their historical range (Crawford and Bolen 1976, Taylor and Guthery 1980a), with recent estimates of current occupied range totaling approximately 17% of the estimated area of their historical range. Causes for this reduction in occupied range are primarily attributed to habitat loss and fragmentation (USFWS 2012). Habitat loss has been caused by conversion of native prairie to cropland (Bent 1932, Copelin 1963, Taylor and Guthery 1980) and long term fire suppression (Woodward et al. 2001) leading to tree invasion (Fuhlendorf et al. 2002). Grazing management practices would help improve habitat if managed to benefit LEPC. Heavily grazed fields that leave no residual vegetation for broods can be detrimental to LEPC (Sell 1979, Hunt and Best 2010). Habitat fragmentation has resulted from a combination of habitat loss and degradation caused by oil and gas development (Hunt 2004) and suspected effects of wind energy development (Pruett et al. 2009). The LEPC is not thought to occur in Kiowa and Rita Blanca National Grasslands (KRB) (Giesen 2003), however some parcels within the grasslands are managed for LEPC. -
Artemisia Californica Less
I. SPECIES Artemisia californica Less. [Updated 2017] NRCS CODE: Subtribe: Artemisiinae ARCA11 Tribe: Anthemideae (FEIS CODE: Family: Asteraceae ARCAL) Order: Asterales Subclass: Asteridae Class: Magnoliopsida flowering heads spring growth seedling, March 2009 juvenile plant photos A. Montalvo flowering plant, November 2005 mature plant with flower buds August 2010 A. Subspecific taxa None. Artemisia californica Less. var. insularis (Rydb.) Munz is now recognized as Artemisia nesiotica P.H. Raven (Jepson eFlora 2017). B. Synonyms Artemisia abrotanoides Nuttall; A. fischeriana Besser; A. foliosa Nuttall; Crossostephium californicum (Lessing) Rydberg (FNA 2017). C. Common name California sagebrush. The common name refers to its strong, sage-like aroma and endemism to California and Baja California. Other names include: coastal sage, coast sage, coast sagebrush (Painter 2016). D. Taxonomic relationships The FNA (2017) places this species in subgenus Artemisia . The molecular phylogeny of the genus has improved the understanding of relationships among the many species of Artemisia and has, at times, placed the species in subgenus Tridentadae; morphology of the inflorescences and flowers alone does not place this species with its closest relatives (Watson et al. 2002). The detailed phylogeny is not completely resolved (Hayat et al. 2009). E. Related taxa in region There are 18 species and a total of 31 taxa (including infrataxa) of Artemisia in southern California, all of which differ clearly from A. californica in habitat affinity, structure, or both (Munz 1974, Jepson eFlora 2017). Within subgenus Artemisia (as per FNA 2017), A. nesiotica from the Channel Islands is the most similar and was once considered part of A. californica ; it can be distinguished by its wider leaves with flat leaf margins (not rolled under). -
Ecological Site R058AC616MT Thin Breaks (TB) RRU 58A-C 11-14" P.Z
Natural Resources Conservation Service Ecological site R058AC616MT Thin Breaks (TB) RRU 58A-C 11-14" p.z. Accessed: 09/24/2021 General information Provisional. A provisional ecological site description has undergone quality control and quality assurance review. It contains a working state and transition model and enough information to identify the ecological site. Associated sites R058AC049MT Silty-Steep (SiStp) RRU 58A-C 11-14" p.z. (combined R058AC046MT, R058AC047MT & R058AC048MT into this site) R058AC057MT Shallow (Sw) RRU 58A-C 11-14" p.z. R058AC058MT Very Shallow (VSw) RRU 58A-C 11-14" p.z. Table 1. Dominant plant species Tree Not specified Shrub Not specified Herbaceous Not specified Physiographic features This site is typically a complex of several ecological sites, primarily Shallow and Very Shallow. It occurs on steep to very steep slopes, usually in excess of 25 percent. Outcroppings of hard bedrock and soft sedimentary beds are major features. Slope aspect can be any direction and can be significant. Table 2. Representative physiographic features Landforms (1) Esca rpment (2) Bluff (3) Ridge Elevation 2,250–4,500 ft Slope 25% Water table depth 60 in Aspect E, S, W Climatic features Major Land Resource Area (MLRA) 58AC in Montana is considered to have a continental climate characterized by cold winters, hot summers, low humidity, light rainfall, and much sunshine. Extremes in temperature are typical. The climate is the result of this MLRA’s location in the geographic center of North America. There are few natural barriers on the northern Great Plains and the winds move freely across the plains and account for rapid changes in temperature. -
The Advantages of Traditional Chumash Healing
eCAM 2005;2(1)19–23 doi:10.1093/ecam/neh072 Lecture Series The Advantages of Traditional Chumash Healing James D. Adams Jr1 and Cecilia Garcia2 1Department of Molecular Pharmacology and Toxicology, University of Southern California, School of Pharmacy, 1985 Zonal Avenue, PSC 508, Los Angeles and 2Chumash Healer, Granada Hills, CA, USA Chumash healing has been practiced in California for ~13 000 years. Chumash healers treat their patients with prayer, laughter, dreaming, phytotherapy, aromatherapy, healing ceremonies and other techniques. Healing involves first healing the spirit, then healing the body. Chumash people still main- tain their unique identity. Chumash Healers still practice the ancient healing arts in California. This lecture is a brief introduction to Chumash Healing. Keywords: healing – ethnopharmacology – Chumash Introduction prayer has been shown to be beneficial to the majority of patients (1). Prayer comforts patients. At the very least, prayer Traditional Chumash healing starts with God. The Healer may does no harm and costs nothing. While in hospital, the patient use prayer and fasting to invite God to help with the healing. may feel isolated from family and friends. The spirit may not Fasting is a self-denial that enhances the spirituality of the become well quickly. The approach with standard health care Healer, facilitating communication with God. In fact, all healing is that the body is treated and made well. The spirit should then must involve God. The spirit is always involved in the healing follow and recover as well. However, many patients complain process. The reason for this is that many diseases start with of uncertainty with their healing even after their bodies are the spirit. -
Illinois Exotic Species List
Exotic Species in Illinois Descriptions for these exotic species in Illinois will be added to the Web page as time allows for their development. A name followed by an asterisk (*) indicates that a description for that species can currently be found on the Web site. This list does not currently name all of the exotic species in the state, but it does show many of them. It will be updated regularly with additional information. Microbes viral hemorrhagic septicemia Novirhabdovirus sp. West Nile virus Flavivirus sp. Zika virus Flavivirus sp. Fungi oak wilt Ceratocystis fagacearum chestnut blight Cryphonectria parasitica Dutch elm disease Ophiostoma novo-ulmi and Ophiostoma ulmi late blight Phytophthora infestans white-nose syndrome Pseudogymnoascus destructans butternut canker Sirococcus clavigignenti-juglandacearum Plants okra Abelmoschus esculentus velvet-leaf Abutilon theophrastii Amur maple* Acer ginnala Norway maple Acer platanoides sycamore maple Acer pseudoplatanus common yarrow* Achillea millefolium Japanese chaff flower Achyranthes japonica Russian knapweed Acroptilon repens climbing fumitory Adlumia fungosa jointed goat grass Aegilops cylindrica goutweed Aegopodium podagraria horse chestnut Aesculus hippocastanum fool’s parsley Aethusa cynapium crested wheat grass Agropyron cristatum wheat grass Agropyron desertorum corn cockle Agrostemma githago Rhode Island bent grass Agrostis capillaris tree-of-heaven* Ailanthus altissima slender hairgrass Aira caryophyllaea Geneva bugleweed Ajuga genevensis carpet bugleweed* Ajuga reptans mimosa -
Dunes Sagebrush Lizard Habitat
TECHNICAL NOTES U.S. DEPARTMENT OF AGRICULTURE NATURAL RESOURCES CONSERVATION SERVICE NEW MEXICO September, 2011 BIOLOGY TECHNICAL NOTE NO. 53 CRITERIA FOR BRUSH MANAGEMENT (314) in Lesser Prairie-Chicken and Dunes Sagebrush Lizard Habitat Introduction NRCS policy requires that when providing technical and financial assistance NRCS will recommend only conservation treatments that will avoid or minimize adverse effects, and to the extent practicable, provide long-term benefit to federal candidate species (General Manual 190 Part 410.22(E)(7)). This technical note provides the criteria to ensure that the NRCS practice of Brush Management (314) will avoid or minimize any adverse effects to two Candidate Species for Federal listing: the lesser prairie chicken Tympanuchus pallidicinctus (LEPC), and dunes sagebrush lizard Sceloporus arenicolus (DSL). Species Involved The lesser prairie chicken is a species of prairie grouse native to the southern high plains of the U.S.; including the sandhill rangelands of eastern New Mexico. The dunes sagebrush lizard is native only to a small area of southeastern New Mexico and west Texas, with a habitat range that overlaps the lesser prairie chicken range, but only occurs in the sand dune complexes associated with shinnery oak (Quercus havardii Rydb.). Both species’ habitat includes a component of brush: shinnery oak and/or sand sagebrush (Artemisia filifolia Torr.). See Appendix 1 and 2 for more details on each species. Geographic Area Covered by Technical Note No. 53 encompasses private and state lands within the range that supports the dunes sagebrush lizard and lesser prairie chicken habitat. This includes portions of seven counties in New Mexico: Chaves, Curry, De Baca, Eddy, Lea, Roosevelt, and Quay counties. -
Biological Survey of a Prairie Landscape in Montana's Glaciated
Biological Survey of a Prairie Landscape in Montanas Glaciated Plains Final Report Prepared for: Bureau of Land Management Prepared by: Stephen V. Cooper, Catherine Jean and Paul Hendricks December, 2001 Biological Survey of a Prairie Landscape in Montanas Glaciated Plains Final Report 2001 Montana Natural Heritage Program Montana State Library P.O. Box 201800 Helena, Montana 59620-1800 (406) 444-3009 BLM Agreement number 1422E930A960015 Task Order # 25 This document should be cited as: Cooper, S. V., C. Jean and P. Hendricks. 2001. Biological Survey of a Prairie Landscape in Montanas Glaciated Plains. Report to the Bureau of Land Management. Montana Natural Heritage Pro- gram, Helena. 24 pp. plus appendices. Executive Summary Throughout much of the Great Plains, grasslands limited number of Black-tailed Prairie Dog have been converted to agricultural production colonies that provide breeding sites for Burrow- and as a result, tall-grass prairie has been ing Owls. Swift Fox now reoccupies some reduced to mere fragments. While more intact, portions of the landscape following releases the loss of mid - and short- grass prairie has lead during the last decade in Canada. Great Plains to a significant reduction of prairie habitat Toad and Northern Leopard Frog, in decline important for grassland obligate species. During elsewhere, still occupy some wetlands and the last few decades, grassland nesting birds permanent streams. Additional surveys will have shown consistently steeper population likely reveal the presence of other vertebrate declines over a wider geographic area than any species, especially amphibians, reptiles, and other group of North American bird species small mammals, of conservation concern in (Knopf 1994), and this alarming trend has been Montana. -
Sagebrush Establishment on Mine Lands
2000 Billings Land Reclamation Symposium BIG SAGEBRUSH (ARTEMISIA TRIDENTATA) COMMUNITIES - ECOLOGY, IMPORTANCE AND RESTORATION POTENTIAL Stephen B. Monsen and Nancy L. Shaw Abstract Big sagebrush (Artemisia tridentata Nutt.) is the most common and widespread sagebrush species in the Intermountain region. Climatic patterns, elevation gradients, soil characteristics and fire are among the factors regulating the distribution of its three major subspecies. Each of these subspecies is considered a topographic climax dominant. Reproductive strategies of big sagebrush subspecies have evolved that favor the development of both regional and localized populations. Sagebrush communities are extremely valuable natural resources. They provide ground cover and soil stability as well as habitat for various ungulates, birds, reptiles and invertebrates. Species composition of these communities is quite complex and includes plants that interface with more arid and more mesic environments. Large areas of big sagebrush rangelands have been altered by destructive grazing, conversion to introduced perennial grasses through artificial seeding and invasion of annual weeds, principally cheatgrass (Bromus tectorum L.). Dried cheatgrass forms continuous mats of fine fuels that ignite and burn more frequently than native herbs. As a result, extensive tracts of sagebrush between the Sierra Nevada and Rocky Mountains are rapidly being converted to annual grasslands. In some areas recent introductions of perennial weeds are now displacing the annuals. The current weed invasions and their impacts on native ecosystems are recent ecological events of unprecedented magnitude. Restoration of degraded big sagebrush communities and reduction of further losses pose major challenges to land managers. Loss of wildlife habitat and recent invasion of perennial weeds into seedings of introduced species highlight the need to stem losses and restore native vegetation where possible. -
Protocol Silver Sage
Protocol Information Upper Colorado Environmental Plant Center Steve Parr, Manager 5538 RBC 4 Meeker , Colorado 81641 970 878-5003 [email protected] http://plant-materials.nrcs.usda.gov/copmc/ Family Scientific Name: Asteraceae Family Common Name: Sunflower Scientific Name: Artemisia cana Common Name: silver sage Species Code: ARCA13 Ecotype: Maybell Colorado General Distribution: From British Columbia east to Manitoba and south to Colorado Propagation Goal: Plants Propagation Method: Seed Product Type: Propagules (seeds, cuttings, poles, etc.) Propagule Collection: Seed was collected in late fall from third week of October through first two weeks of November via hand stripping or clipping leader growth with seed heads. 846,000 seeds/lb. (Hassell, et al. 1996) Propagule Processing: Seed is placed into a Forsberg for a brief period, then run through a Clipper air cleaner with a number 1/18 screen on the top and a blank screen on the bottom. Air speed is set at low and entire process is continued until desired seed cleanness is achieved. Pre-Planting Treatments: No treatment necessary Growing Area Preparation/ Annual Practices for Perennial Crops: Firm, weed free seed bed. Shallow (less than 1cm) planting depth with limited irrigation through germination and periodically throughout growing season until plants are established. Establishment Phase: Sowing/Planting Technique: Seeded with a belt seeder Length of Establishment Phase: Can begin producing seed between year two or three. Active Growth Phase: Spring and summer are active growth times. Harvesting, Storage and Shipping: Seed can be hand collected or clipped from the plant late in the year, October through November.