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Yellowstone National Park, Resources and Issues, Vegetation
VEGETATION More than 1,300 plant taxa occur in Yellowstone National Park. The whitebark pine, shown here and found in high elevations in the Greater Yellowstone Ecosystem, is an important native species in decline. Vegetation The vegetation communities of Yellowstone National major disturbances. Yellowstone is home to three Park include overlapping combinations of species endemic plant species, at least two of which depend typical of the Rocky Mountains as well as of the on the unusual habitat created by the park’s thermal Great Plains to the east and the Intermountain region features. Most vegetation management in the park to the west. The exact vegetation community pres- is focused on minimizing human-caused impacts on ent in any area of the park reflects the consequences their native plant communities to the extent feasible. of the underlying geology, ongoing climate change, substrates and soils, and disturbances created by fire, Vegetation Communities floods, landslides, blowdowns, insect infestations, There are several vegetation communities in and the arrival of nonnative plants. Yellowstone: higher- and lower-elevation forests Today, the roughly 1,386 native taxa in the park and the understory vegetation associated with them, represent the species able to either persist in the area sagebrush-steppe, wetlands, and hydrothermal. or recolonize after glaciers, lava flows, and other Quick Facts Number in Yellowstone • Three endemic species (found only Management Issues Native plant taxa: more than 1,300: in Yellowstone): Ross’s bentgrass, • Controlling nonnative species, • Hundreds of wildfowers. Yellowstone sand verbena, which threaten native species, Yellowstone sulfur wild buckwheat. especially near developed areas; • Trees: nine conifers (lodgepole some are spreading into the Nonnative plant species: 225. -
The Introduction of Pinus Contorta in Sweden
The Introduction of Pinus contorta in Sweden Implications for forest diversity Sofia Bäcklund Faculty of Forest Sciences Department of Ecology Uppsala Doctoral Thesis Swedish University of Agricultural Sciences Uppsala 2016 Acta Universitatis Agriculturae Sueciae 2016:30 Cover: A 15-year old Pinus contorta stand. Dorotea, Sweden (photo: S. Bäcklund) ISSN 1652-6880 ISBN (print version) 978-91-576-8562-9 ISBN (electronic version) 978-91-576-8563-6 © 2016 Sofia Bäcklund, Uppsala Print: SLU Service/Repro, Uppsala 2016 The introduction of Pinus contorta in Sweden. Implications for forest diversity Abstract An increasing demand for forest-based products calls for further development and intensification of forest management. The use of non-native tree species in forestry is a common and expanding silvicultural practice worldwide but the effect of non-native trees on native biodiversity and ecosystem functioning is still poorly understood. The general aim of this thesis is to increase our knowledge about what effects large-scale introduction of a non-native tree species have on forest biodiversity over a chronosequence of forest stand ages. The non-native Pinus contorta and the two native tree species Pinus sylvestris and Picea abies were studied over three age classes (15, 30, 85 years old) of managed forests in northern Sweden to compare the stand- and tree structures, the cover and composition of functional groups of ground vegetation, and the species- and functional diversity of epiphytic lichens. Differences in ground vegetation cover were linked to both tree species and different stand and tree characteristics, but the differences were not consistent over the age classes. -
Carbon Sequestration in Managed Temperate Coniferous Forests Under Climate Change
Biogeosciences, 13, 1933–1947, 2016 www.biogeosciences.net/13/1933/2016/ doi:10.5194/bg-13-1933-2016 © Author(s) 2016. CC Attribution 3.0 License. Carbon sequestration in managed temperate coniferous forests under climate change Caren C. Dymond1, Sarah Beukema2, Craig R. Nitschke3, K. David Coates1, and Robert M. Scheller4 1Ministry of Forests, Lands and Natural Resource Operations, Government of British Columbia, Victoria, Canada 2ESSA Technologies Ltd., Vancouver, Canada 3School of Ecosystem and Forest Sciences, University of Melbourne, Richmond, Australia 4Department of Environmental Science and Management, Portland State University, Portland, USA Correspondence to: Caren C. Dymond ([email protected]) Received: 16 November 2015 – Published in Biogeosciences Discuss.: 21 December 2015 Revised: 11 March 2016 – Accepted: 16 March 2016 – Published: 30 March 2016 Abstract. Management of temperate forests has the poten- 1 Introduction tial to increase carbon sinks and mitigate climate change. However, those opportunities may be confounded by nega- tive climate change impacts. We therefore need a better un- As a global society, we depend on forests and land to take −1 derstanding of climate change alterations to temperate for- up about 2.5 C 1.3 PgC yr , about one-third of our fossil est carbon dynamics before developing mitigation strategies. emissions (Ciais et al., 2013). A reduction in the size of The purpose of this project was to investigate the interac- these sinks could accelerate global change by further increas- tions of species composition, fire, management, and climate ing the accumulation rate of greenhouse gases in the atmo- change in the Copper–Pine Creek valley, a temperate conifer- sphere. -
Shrubl Maritime Juniper Woodland/Shrubland
Maritime Juniper Woodland/ShrublWoodland/Shrublandand State Rank: S1 – Critically Imperiled The Maritime Juniper Woodland/ substrate stability; even Shrubland is a predominantly evergreen in stable situations community within the coastal salt spray community edges may zone; The trees tend to be short (less not be clear. Different than 15 feet) and scattered, with the types of communities tops sculpted by winds and salt spray; grade into and interdigitate with each forests, in areas of continuous changes of other. Very small patches levels of salt spray and substrate types. of any type within The dominant species is eastern red cedar another community (also called juniper), though the should be considered to Maritime Juniper Woodland/Shrubland above a abundance of red cedar is highly variable. be part of the variation of salt marsh. Photo: Patricia Swain, NHESP. It grows in association with scattered trees the main community. Description: Maritime Juniper and shrubs typical of the surrounding Maritime Pitch Pine Woodland/Shrublands occur on and vegetation such as pitch pine, various Woodlands on Dunes are between sand dunes, on the upper edges oaks, black cherry, red maple, blueberries, dominated by pitch pine. Maritime provide habitat for shrubland nesting birds of salt marshes and on cliffs and rocky huckleberries, sumac, and very often, Shrubland communities are dominated by and are important as feeding and resting/ headlands: all areas receiving salt spray poison ivy. Green briar can be abundant in a dense mixture of primarily deciduous roosting areas for migrating birds. from high winds. The maritime juniper more established woodlands, particularly shrubs, but may include red cedar. -
Global Ecological Forest Classification and Forest Protected Area Gap Analysis
United Nations Environment Programme World Conservation Monitoring Centre Global Ecological Forest Classification and Forest Protected Area Gap Analysis Analyses and recommendations in view of the 10% target for forest protection under the Convention on Biological Diversity (CBD) 2nd revised edition, January 2009 Global Ecological Forest Classification and Forest Protected Area Gap Analysis Analyses and recommendations in view of the 10% target for forest protection under the Convention on Biological Diversity (CBD) Report prepared by: United Nations Environment Programme World Conservation Monitoring Centre (UNEP-WCMC) World Wide Fund for Nature (WWF) Network World Resources Institute (WRI) Institute of Forest and Environmental Policy (IFP) University of Freiburg Freiburg University Press 2nd revised edition, January 2009 The United Nations Environment Programme World Conservation Monitoring Centre (UNEP- WCMC) is the biodiversity assessment and policy implementation arm of the United Nations Environment Programme (UNEP), the world's foremost intergovernmental environmental organization. The Centre has been in operation since 1989, combining scientific research with practical policy advice. UNEP-WCMC provides objective, scientifically rigorous products and services to help decision makers recognize the value of biodiversity and apply this knowledge to all that they do. Its core business is managing data about ecosystems and biodiversity, interpreting and analysing that data to provide assessments and policy analysis, and making the results -
Stuart, Trees & Shrubs
Excerpted from ©2001 by the Regents of the University of California. All rights reserved. May not be copied or reused without express written permission of the publisher. click here to BUY THIS BOOK INTRODUCTION HOW THE BOOK IS ORGANIZED Conifers and broadleaved trees and shrubs are treated separately in this book. Each group has its own set of keys to genera and species, as well as plant descriptions. Plant descriptions are or- ganized alphabetically by genus and then by species. In a few cases, we have included separate subspecies or varieties. Gen- era in which we include more than one species have short generic descriptions and species keys. Detailed species descrip- tions follow the generic descriptions. A species description in- cludes growth habit, distinctive characteristics, habitat, range (including a map), and remarks. Most species descriptions have an illustration showing leaves and either cones, flowers, or fruits. Illustrations were drawn from fresh specimens with the intent of showing diagnostic characteristics. Plant rarity is based on rankings derived from the California Native Plant Society and federal and state lists (Skinner and Pavlik 1994). Two lists are presented in the appendixes. The first is a list of species grouped by distinctive morphological features. The second is a checklist of trees and shrubs indexed alphabetically by family, genus, species, and common name. CLASSIFICATION To classify is a natural human trait. It is our nature to place ob- jects into similar groups and to place those groups into a hier- 1 TABLE 1 CLASSIFICATION HIERARCHY OF A CONIFER AND A BROADLEAVED TREE Taxonomic rank Conifer Broadleaved tree Kingdom Plantae Plantae Division Pinophyta Magnoliophyta Class Pinopsida Magnoliopsida Order Pinales Sapindales Family Pinaceae Aceraceae Genus Abies Acer Species epithet magnifica glabrum Variety shastensis torreyi Common name Shasta red fir mountain maple archy. -
Connon Nurseries Taylor's Sunburst Lodgepole Pine
Taylor's Sunburst Lodgepole Pine Pinus contorta 'Taylor's Sunburst' Height: 15 feet Spread: 10 feet Sunlight: Hardiness Zone: 4a Description: Wow! When you see this pine tree, you want it - the bright yellow-gold new growth contrasts stunningly with the older green needles for nearly two months in spring, then come the bright red cones; this plant is certain to turn heads in your landscape Ornamental Features Taylor's Sunburst Lodgepole Pine foliage Taylor's Sunburst Lodgepole Pine has attractive green foliage which Photo courtesy of NetPS Plant Finder emerges yellow in spring. The needles are highly ornamental and remain green throughout the winter. The red fruits are held in cones in mid summer. The flowers are not ornamentally significant. The shaggy brick red bark adds an interesting dimension to the landscape. Landscape Attributes Taylor's Sunburst Lodgepole Pine is a multi-stemmed evergreen shrub with an upright spreading habit of growth. Its average texture blends into the landscape, but can be balanced by one or two finer or coarser trees or shrubs for an effective composition. This is a relatively low maintenance shrub. When pruning is necessary, it is recommended to only trim back the new growth of the current season, other than to remove any dieback. It has no significant negative characteristics. Taylor's Sunburst Lodgepole Pine is recommended for the following landscape applications; - Accent - Vertical Accent - General Garden Use Planting & Growing Taylor's Sunburst Lodgepole Pine will grow to be about 15 feet tall at maturity, with a spread of 10 feet. It has a low canopy, and is suitable for planting under power lines. -
Influence of Fire Interval and Serotiny on Postfire Lodgepole Pine Density in Yellowstone National Park
Utah State University DigitalCommons@USU Quinney Natural Resources Research Library, The Bark Beetles, Fuels, and Fire Bibliography S.J. and Jessie E. 2003 Influence of Fire Interval and Serotiny on Postfire Lodgepole Pine Density in Yellowstone National Park Tania Schoennagel Monica G. Turner William H. Romme Follow this and additional works at: https://digitalcommons.usu.edu/barkbeetles Part of the Ecology and Evolutionary Biology Commons, Entomology Commons, Forest Biology Commons, Forest Management Commons, and the Wood Science and Pulp, Paper Technology Commons Recommended Citation Schoennagel, T., Turner, M. and Romme, W. (2003). Influence of fire interval and serotiny on postfire lodgepole pine density in Yellowstone National Park. Ecology, 84(11): 2967—2978. This Article is brought to you for free and open access by the Quinney Natural Resources Research Library, S.J. and Jessie E. at DigitalCommons@USU. It has been accepted for inclusion in The Bark Beetles, Fuels, and Fire Bibliography by an authorized administrator of DigitalCommons@USU. For more information, please contact [email protected]. Ecology, 84(11), 2003, pp. 2967±2978 q 2003 by the Ecological Society of America THE INFLUENCE OF FIRE INTERVAL AND SEROTINY ON POSTFIRE LODGEPOLE PINE DENSITY IN YELLOWSTONE NATIONAL PARK TANIA SCHOENNAGEL,1,3 MONICA G. TURNER,1 AND WILLIAM H. ROMME2 1Department of Zoology, University of Wisconsin, Madison, Wisconsin 53706 USA 2Department of Forest Sciences, Colorado State University, Fort Collins, Colorado 80523 USA Abstract. The time interval between stand-replacing ®res can in¯uence patterns of initial post®re succession if the abundance of post®re propagules varies with pre®re stand age. -
NFI Woodland Ecological Condition Scoring Methodology
NFI woodland ecological condition in Great Britain: Methodology National Forest Inventory Issued by: National Forest Inventory, Forestry Commission, 231 Corstorphine Road, Edinburgh, EH12 7AT Date: February 2020 Enquiries: Ben Ditchburn, 0300 067 5561 [email protected] Statistician: David Ross [email protected] Website: www.forestresearch.gov.uk/inventory www.forestresearch.gov.uk/forecast NFI woodland ecological condition methodology Contents Introduction ...................................................................................................... 5 The NFI .......................................................................................................... 6 Why report on woodland ecological condition? ...................................................... 7 Development of the NFI condition monitoring approach .......................................... 9 Assessing broad and priority woodland habitat condition ...................................... 9 NFI WEC indicator selection .......................................................................... 10 Classifying and scoring woodlands ................................................................. 14 A straightforward, transparent and evidence-informed approach ......................... 15 Methodology .................................................................................................... 16 Categorising woodland area for reporting ........................................................... 16 Defining the native woodland -
Douglas- Fir Limber Pine Lodgepole Pine Ponderosa Pine Blue Spruce
NAME ORIGIN BARK FEMALE CONES NEEDLES WHERE USES TRIVIA Named by Smooth gray bark To 4ÂÂ long, Soft, flat, 2-sided, Found on north or Railroad crossties, State tree of Scottish botanist on young trees yellowish to light 1¼″ long and south-facing slopes, mine timbers, for Oregon. David Douglas. with numerous brown hanging cones rounded at the tip. in shady ravines and building ships and The Latin name DOUGLAS- Fir is from the resin scars. with uniquely 3- Dark yellow green or on rocky slopes boats, construction psuedotsuga Middle English pointed bracts blue green. Shortly where the soil is lumber, plywood, means FIR firre and Old protruding from cone stalked spreading fairly deep. telephone poles, ÂÂfalse Psuedotsuga English fyrh. scales like a snakes- mostly in two rows. fencing, railroad-car fir.ÂÂ menziesii tongue. Single small groove construction, boxes Can drop 2 on topside of needles and crates, flooring, million seeds in and single white line furniture, ladders a good year. on underside of and pulpwood. needles. Pine is from the Light gray to Big (to 9ÂÂ long) Stout in clusters of 5 Found on rocky, Lumber, railroad Cones start to LIMBER Latin pinus and blackish brown. cylindrical, greenish needles, to 3″ long. gravelly slopes, cross ties, poles, appear after the the Old English Smooth and silvery brown, with thick, Straight or slightly ridges and peaks. turpentine, tar and tree reaches 20 PINE pin. gray on young broad scales. Cone curved, not sticky to fuel. years of age. Pinus flexilis trees. scales lack prickles. the touch. Dark green. Pine is from the Bark is grayish or Light yellow brown, Stout, twisted Found in well Lumber, knotty Many Plains Latin pinus and light brown, thin reddish or dark green, needles, mostly in drained soils, dry pine paneling, Indian tribes the Old English and with many lopsided cones to pairs, to 2½″ long. -
Black-Tailed Praire Dog Surveys in Pueblo, Crowley, Otero
BLACK-TAILED PRAIRIE DOG SURVEYS OF BLM LANDS IN EASTERN COLORADO A Report to the Bureau of Land Management, Canon City Office By The Colorado Natural Heritage Program Colorado State University March 2004 Timothy J Assal and John R Sovell Colorado Natural Heritage Program Colorado State University 8002 Campus Delivery Fort Collins, Colorado 80523-8002 TABLE OF CONTENTS INTRODUCTION…………………………………………………………………………….…4 METHODS……………………………………………………………………………………….6 RESULTS………………………………………………………………………………………...7 Study Area………………………………………………………………………………………7 Element Occurrences of Animals Tracked by CNHP………………………………………….11 Parcel Summaries………………………………………………………………………………17 Baca County………………………………………………………………………………..15 Bent County..…………………………………………...……………………………....….21 El Paso County..…………………………………………………………….…...…………27 Kiowa County…………………………………………………………………...…………29 Las Animas County………………………………………………………………………...33 Lincoln County…………………………………………………………..………………...39 Logan County………………………………………………..……………………………..45 Morgan County………………..…………………………………………………………...47 Prowers County…..…………….…………………………………………………………..51 Sedgwick County…………………………………………………………………………..55 Washington County…….………………………………………………………………….57 Weld County………………….……………………………………………………………59 Yuma County………………………………………………………………………………61 Potential Conservation Areas….…………………………………………………………...65 B2 Potential Conservation Areas………………………………………………………...65 Chico Basin Shortgrass Prairie..……………………………………………………..65 Jesus Mesa……...…………………………………………………………………....71 Neeskah…….………….………………………………………………….………….75 Signal -
San Francisco Mountains Forest Heserve, Arizona
Professional Paper No. 22 Series H, Forestry, 7 DEPARTMENT OF THE INTERIOR UNITED STATES GEOLOGICAL SURVEY CHARLES D. WALCOTT, DIRECTOR \ FOREST CONDITIONS lN 'fHE- SAN FRANCISCO MOUNTAINS FOREST HESERVE, ARIZONA BY JOHN B. LEIBERG, THEODORE F. RIXON, AND ARTHUR DODWELL WITH AN INTRODUCTION BY F. G. PLUMMER ·wASHINGTON G 0 Y E R N 1\I E N T I' HI N T IN G 0 ];' F I C E 1904 CONT .. ENTS. Page.. Letter of transmittaL_. __._._. ____-_._._._ .. _._ .. _.. _. ______ . __ _._._._- __._. ________ ._· __________ .~ __ . ____ . __ .___ 9 Introdnetion.·.-_-_. ______________ ._._._._._._._. ___ .. _______ .___ -_._. __ . ___________ . ____ . _. _________ ---- _ ___ 11 Boundaries·. ___ .----- ___ .·.·-·-·-·-·-·-·-_._. __ . __________ ._ .. _.._._. ______ . _______________ . _____ .___ 11 Surface features ___ . _ _- ..·: ______ ._._._ ..·.- ___ .· _ _. _ _. __ . _ _. ___________ .: ___________ . ________ ._______ 13 Soil·. _. _: _. _.. __ _. .. _ . _. __ .. __. .· ..· .... _. _. _..: ____ _. __. __ _. .· __.. __ . ___ .. __ . __ . __ . __ .. _____ . ___ .. 15 Drainage_._. _ _. ___ . _____________________ . __________ _.:. _ _. ________ . ____ . ___ ------_________ 15 Forest and womllan<.l .· __ . __ . __ . __ . __ . _____ ·- : _.. ·_____ . ___________ . ____ .· __ . _____ . _....... _ _ 17 Zones or types of arborescent growth_ . _.·. _. __.: _. __ . _: __. ... ____ . _______ . __ . __ . _.. _.. ___ . _ 18 Aspect and character of timber belts ____ .