Mapping Vegetation Types in a Savanna Ecosystem in Namibia: Concepts for Integrated Land Cover Assessments
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Grassland & Shrubland Vegetation
Grassland & Shrubland Vegetation Missoula Draft Resource Management Plan Handout May 2019 Key Points Approximately 3% of BLM-managed lands in the planning area are non-forested (less than 10% canopy cover); the other 97% are dominated by a forested canopy with limited mountain meadows, shrublands, and grasslands. See table 1 on the following page for a break-down of BLM-managed grassland and shrubland in the planning area classified under the National Vegetation Classification System (NVCS). The overall management goal of grassland and shrubland resources is to maintain diverse upland ecological conditions while providing for a variety of multiple uses that are economically and biologically feasible. Alternatives Alternative A (1986 Garnet RMP, as Amended) Maintain, or where practical enhance, site productivity on all public land available for livestock grazing: (a) maintain current vegetative condition in “maintain” and “custodial” category allotments; (b) improve unsatisfactory vegetative conditions by one condition class in certain “improvement” category allotments; (c) prevent noxious weeds from invading new areas; and, (d) limit utilization levels to provide for plant maintenance. Alternatives B & C (common to all) Proposed objectives: Manage uplands to meet health standards and meet or exceed proper functioning condition within site or ecological capability. Where appropriate, fire would be used as a management agent to achieve/maintain disturbance regimes supporting healthy functioning vegetative conditions. Manage surface-disturbing activities in a manner to minimize degradation to rangelands and soil quality. Mange areas to conserve BLM special status species plants. Ensure consistency with achieving or maintaining Standards of Rangeland Health and Guidelines for Livestock Grazing Management for Montana, North Dakota, and South Dakota. -
Land Cover Austin, TX This Enviroatlas Map Shows Land Cover for the Austin, TX Area at High Spatial Resolution (1-Meter Pixels)
• Austin, TX • New Haven, CT • Baltimore, MD • New York, NY • Birmingham, AL • Paterson, NJ • Brownsville, TX • Philadelphia, PA • Chicago, IL • Phoenix, AZ • Cleveland, OH • Pittsburgh, PA • Des Moines, IA • Portland, ME • Durham, NC • Portland, OR • Fresno, CA • Salt Lake City, UT • Green Bay, WI • Sonoma County, CA • Los Angeles, CA • St Louis, MO • Memphis, TN • Tampa, FL • Milwaukee, WI • Virginia Beach, VA • Minneapolis, MN • Washington, DC • New Bedford, MA • Woodbine, IA Meter Scale Urban Land Cover Austin, TX This EnviroAtlas map shows land cover for the Austin, TX area at high spatial resolution (1-meter pixels). The land cover classes are Water, Impervious Surface, Soil and Barren, Trees and Forest, Grass and Herbaceous, and Agriculture.1 Why is high resolution land cover important? Land cover data present a “birds-eye” view that can help identify important features, patterns and relationships in the landscape. The National Land Cover Dataset (NLCD)2 provides land cover for the entire contiguous U.S. at 30- meter pixel resolution. However, for some analyses, the density and heterogeneity of an urban landscape requires higher resolution land cover data. Meter Scale Urban Land Cover (MULC) data were developed to fulfill that need. In comparison, there are 900 MULC pixels for every one NLCD pixel. Anticipated users of MULC include city and regional planners, water authorities, wildlife and natural resource Figure 2: MULC for Austin, managers, public health officials, citizens, teachers, and TX. students. Potential applications of these data include the How can I use this information? assessment of wildlife corridors and riparian buffers, This data layer can be used alone or combined visually and stormwater management, urban heat island mitigation, access analytically with other spatial data layers. -
Large Scale High-Resolution Land Cover Mapping with Multi-Resolution Data
Large Scale High-Resolution Land Cover Mapping with Multi-Resolution Data Caleb Robinson Le Hou Kolya Malkin Georgia Institute of Technology Stony Brook University Yale University Rachel Soobitsky Jacob Czawlytko Bistra Dilkina Chesapeake Conservancy Chesapeake Conservancy University of Southern California Nebojsa Jojic∗ Microsoft Research Abstract uses include informing agricultural best management practices, monitoring forest change over time [10] and measuring urban In this paper we propose multi-resolution data fusion meth- sprawl [31]. However, land cover maps quickly fall out of ods for deep learning-based high-resolution land cover map- date and must be updated as construction, erosion, and other ping from aerial imagery. The land cover mapping problem, at processes act on the landscape. country-level scales, is challenging for common deep learning In this work we identify the challenges in automatic methods due to the scarcity of high-resolution labels, as well large-scale high-resolution land cover mapping and de- as variation in geography and quality of input images. On the velop methods to overcome them. As an application of other hand, multiple satellite imagery and low-resolution ground our methods, we produce the first high-resolution (1m) truth label sources are widely available, and can be used to land cover map of the contiguous United States. We have improve model training efforts. Our methods include: introduc- released code used for training and testing our models at ing low-resolution satellite data to smooth quality differences https://github.com/calebrob6/land-cover. in high-resolution input, exploiting low-resolution labels with a dual loss function, and pairing scarce high-resolution labels Scale and cost of existing data: Manual and semi-manual with inputs from several points in time. -
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. -
Edition 2 from Forest to Fjaeldmark the Vegetation Communities Highland Treeless Vegetation
Edition 2 From Forest to Fjaeldmark The Vegetation Communities Highland treeless vegetation Richea scoparia Edition 2 From Forest to Fjaeldmark 1 Highland treeless vegetation Community (Code) Page Alpine coniferous heathland (HCH) 4 Cushion moorland (HCM) 6 Eastern alpine heathland (HHE) 8 Eastern alpine sedgeland (HSE) 10 Eastern alpine vegetation (undifferentiated) (HUE) 12 Western alpine heathland (HHW) 13 Western alpine sedgeland/herbland (HSW) 15 General description Rainforest and related scrub, Dry eucalypt forest and woodland, Scrub, heathland and coastal complexes. Highland treeless vegetation communities occur Likewise, some non-forest communities with wide within the alpine zone where the growth of trees is environmental amplitudes, such as wetlands, may be impeded by climatic factors. The altitude above found in alpine areas. which trees cannot survive varies between approximately 700 m in the south-west to over The boundaries between alpine vegetation communities are usually well defined, but 1 400 m in the north-east highlands; its exact location depends on a number of factors. In many communities may occur in a tight mosaic. In these parts of Tasmania the boundary is not well defined. situations, mapping community boundaries at Sometimes tree lines are inverted due to exposure 1:25 000 may not be feasible. This is particularly the or frost hollows. problem in the eastern highlands; the class Eastern alpine vegetation (undifferentiated) (HUE) is used in There are seven specific highland heathland, those areas where remote sensing does not provide sedgeland and moorland mapping communities, sufficient resolution. including one undifferentiated class. Other highland treeless vegetation such as grasslands, herbfields, A minor revision in 2017 added information on the grassy sedgelands and wetlands are described in occurrence of peatland pool complexes, and other sections. -
Existing Vegetation Classification and Mapping
Existing Vegetation Classification and Mapping Technical Guide Version 1.0 Guide Version Classification and Mapping Technical Existing Vegetation United States Department of Agriculture Existing Vegetation Forest Service Classification and Ecosystem Management Coordination Staff Mapping Technical Guide Gen. Tech. Report WO-67 Version 1.0 April 2005 United States Department of Agriculture Existing Vegetation Forest Service Classification and Ecosystem Management Coordination Staff Mapping Technical Guide Gen. Tech. Report WO-67 Version 1.0 April 2005 Ronald J. Brohman and Larry D. Bryant Technical Editors and Coordinators Authored by: Section 1: Existing Vegetation Classification and Mapping Framework David Tart, Clinton K. Williams, C. Kenneth Brewer, Jeff P. DiBenedetto, and Brian Schwind Section 2: Existing Vegetation Classification Protocol David Tart, Clinton K. Williams, Jeff P. DiBenedetto, Elizabeth Crowe, Michele M. Girard, Hazel Gordon, Kathy Sleavin, Mary E. Manning, John Haglund, Bruce Short, and David L. Wheeler Section 3: Existing Vegetation Mapping Protocol C. Kenneth Brewer, Brian Schwind, Ralph J. Warbington, William Clerke, Patricia C. Krosse, Lowell H. Suring, and Michael Schanta Team Members Technical Editors Ronald J. Brohman National Resource Information Requirements Coordinator, Washington Office Larry D. Bryant Assistant Director, Forest and Range Management Staff, Washington Office Authors David Tart Regional Vegetation Ecologist, Intermountain Region, Ogden, UT C. Kenneth Brewer Landscape Ecologist/Remote Sensing Specialist, Northern Region, Missoula, MT Brian Schwind Remote Sensing Specialist, Pacific Southwest Region, Sacramento, CA Clinton K. Williams Plant Ecologist, Intermountain Region, Ogden, UT Ralph J. Warbington Remote Sensing Lab Manager, Pacific Southwest Region, Sacramento, CA Jeff P. DiBenedetto Ecologist, Custer National Forest, Billings, MT Elizabeth Crowe Riparian/Wetland Ecologist, Deschutes National Forest, Bend, OR William Clerke Remote Sensing Program Manager, Southern Region, Atlanta GA Michele M. -
Chapter 3 Vegetation Diversity 3
Chapter 3 Vegetation Diversity Vegetation Diversity INTRODUCTION Biodiversity has been defined as the variety of living organisms; the genetic differences among them; and the communities, ecosystems and landscapes in which they occur (Noss 1990, West 1995). Biodiversity has leapt to the forefront of issues due to a variety of reasons; changing societal values, accelerated species extinctions, global environmental change, aesthetic values, and the value of goods and services supplied (West 1995). Maintenance of ecological functions, processes, and disturbance regimes is as important as preserving species, their populations, genetic structure, biotic communities, and landscapes. Hence ecosystem-level processes, services, and disturbances must be considered within the arena of biodiversity concerns (West and Whitford 1995). The biological diversity that is supported by a particular area is generally a positive function of the degree of environmental heterogeneity occurring over space and time within that area (Longland and Young 1995). Vegetation is a cornerstone of biological diversity. Vegetation exerts its influence into almost every facet of the biophysical world. Many biophysical processes and functions depend on or are connected to vegetative conditions. Vegetation is an integral part of ecosystem composition, function, and structure. Vegetation shapes and in turn, is shaped by the ecosystems in which it occurs. It provides plant and animal habitat, and determines wildfire and insect hazards. Leaves, branches, and roots contribute to soil productivity and stability. Large wood in streams increases physical complexity, providing more habitat diversity. Vegetation shades streams, helping to maintain desirable water temperature, and also acts as a physical and biological barrier or filter for sediment and debris flowing from adjacent hillsides toward streams. -
7. Shrubland and Young Forest Habitat Management
7. SHRUBLAND AND YOUNG FOREST HABITAT MANAGEMENT hrublands” and “Young Forest” are terms that apply to areas Shrubland habitat and that are transitioning to mature forest and are dominated by young forest differ in “Sseedlings, saplings, and shrubs with interspersed grasses and forbs (herbaceous plants). While some sites such as wetlands, sandy sites vegetation types and and ledge areas can support a relatively stable shrub cover, most shrub communities in the northeast are successional and change rapidly to food and cover they mature forest if left unmanaged. Shrub and young forest habitats in Vermont provide important habitat provide, as well as functions for a variety of wildlife including shrubland birds, butterflies and bees, black bear, deer, moose, snowshoe hare, bobcat, as well as a where and how they variety of reptiles and amphibians. Many shrubland species are in decline due to loss of habitat. Shrubland bird species in Vermont include common are maintained on the species such as chestnut-sided warbler, white-throated sparrow, ruffed grouse, Eastern towhee, American woodcock, brown thrasher, Nashville landscape. warbler, and rarer species such as prairie warbler and golden-winged warbler. These habitat types are used by 29 Vermont Species of Greatest Conservation Need. While small areas of shrub and young forest habitat can be important to some wildlife, managing large patches of 5 acres or more provides much greater benefit to the wildlife that rely on the associated habitat conditions to meet their life requirements. Birds such as the chestnut- sided warbler will use smaller areas of young forest, but less common species such as golden-winged warbler require areas of 25 acres or more. -
Ecoveg: a New Approach to Vegetation Description and Classification
REVIEWS Ecological Monographs, 84(4), 2014, pp. 533–561 Ó 2014 by the Ecological Society of America EcoVeg: a new approach to vegetation description and classification 1,11 2 3,12 4 5 DON FABER-LANGENDOEN, TODD KEELER-WOLF, DEL MEIDINGER, DAVE TART, BRUCE HOAGLAND, CARMEN 1 6 7 8 9 10 JOSSE, GONZALO NAVARRO, SERGUEI PONOMARENKO, JEAN-PIERRE SAUCIER, ALAN WEAKLEY, AND PATRICK COMER 1NatureServe, Conservation Science Division, 4600 North Fairfax Drive, Arlington, Virginia 22203 USA 2Biogeographic Data Branch, California Department of Fish and Game, Sacramento, California 95814 USA 3British Columbia Ministry of Forests and Range, Research Branch, Victoria, British Columbia V8W 9C2 Canada 4USDA Forest Service, Intermountain Region, Natural Resources, Ogden, Utah 84401 USA 5Oklahoma Biological Survey and Department of Geography, University of Oklahoma, Norman, Oklahoma 73019 USA 6Universidad Cato´lica Boliviana San Pablo, Unidad Acade´mica Regional Cochabamba Departamento de Ciencias Exactas e Ingenierı´as, Carrera de Ingenierı´a Ambiental, Cochabamba, Bolivia 7Ecological Integrity Branch, Parks Canada, Rue Eddy, Gatineau, Quebec K1A 0M5 Canada 8Ministe`re des Ressources Naturelles 2700, Rue Einstein, Bureau B-1-185, Quebec City, Quebec G1P 3W8 Canada 9North Carolina Botanic Garden, University of North Carolina, Chapel Hill, North Carolina 27599 USA 10NatureServe, 2108 55th Street, Boulder, Colorado 80301 USA Abstract. A vegetation classification approach is needed that can describe the diversity of terrestrial ecosystems and their transformations over large time frames, span the full range of spatial and geographic scales across the globe, and provide knowledge of reference conditions and current states of ecosystems required to make decisions about conservation and resource management. -
Glossary and Acronyms Glossary Glossary
Glossary andChapter Acronyms 1 ©Kevin Fleming ©Kevin Horseshoe crab eggs Glossary and Acronyms Glossary Glossary 40% Migratory Bird “If a refuge, or portion thereof, has been designated, acquired, reserved, or set Hunting Rule: apart as an inviolate sanctuary, we may only allow hunting of migratory game birds on no more than 40 percent of that refuge, or portion, at any one time unless we find that taking of any such species in more than 40 percent of such area would be beneficial to the species (16 U.S.C. 668dd(d)(1)(A), National Wildlife Refuge System Administration Act; 16 U.S.C. 703-712, Migratory Bird Treaty Act; and 16 U.S.C. 715a-715r, Migratory Bird Conservation Act). Abiotic: Not biotic; often referring to the nonliving components of the ecosystem such as water, rocks, and mineral soil. Access: Reasonable availability of and opportunity to participate in quality wildlife- dependent recreation. Accessibility: The state or quality of being easily approached or entered, particularly as it relates to complying with the Americans with Disabilities Act. Accessible facilities: Structures accessible for most people with disabilities without assistance; facilities that meet Uniform Federal Accessibility Standards; Americans with Disabilities Act-accessible. [E.g., parking lots, trails, pathways, ramps, picnic and camping areas, restrooms, boating facilities (docks, piers, gangways), fishing facilities, playgrounds, amphitheaters, exhibits, audiovisual programs, and wayside sites.] Acetylcholinesterase: An enzyme that breaks down the neurotransmitter acetycholine to choline and acetate. Acetylcholinesterase is secreted by nerve cells at synapses and by muscle cells at neuromuscular junctions. Organophosphorus insecticides act as anti- acetyl cholinesterases by inhibiting the action of cholinesterase thereby causing neurological damage in organisms. -
Ecological Land Cover and Natural Resources Inventory for the Kansas City Region
Ecological Land Cover and Natural Resources Inventory for the Kansas City Region 2. Ecological Land Cover Assessment and Natural Resource Inventory Methods This section describes the general approach and methodology used to complete the ecological classification and inventory for the Kansas City region. Applied Ecological Services, Inc. (AES) used the following tasks to complete the ecological survey and inventory, which are described in detail in the following sub-sections: 1. Data Assembly and Mapping: digital information from several government sources was used to establish baseline information about land cover in the region. 2. Field Reconnaissance: The digital information was validated and/or refined through field inspections and verifications. 3. Ecological Land Cover Classification Development: Using data from the data assembly and subsequent field reconnaissance, AES created an ecological classification representing existing natural resources in the region, a GIS-based information database, and a regional map of ecological land cover. 4. Data Extrapolation and Second Field Verification: The ecological classification involved an iterative process in which initial data were assembled, evaluated in the field, revised, and then re-evaluated in the field a second time. Final data were assembled after the second field reconnaissance, evaluated, and incorporated into the GIS program and the regional land cover map. Details of the methodology of this process are provided in Appendix A. This program was completed between June 2003 and June 2004. 2.1. Data Assembly and Base Mapping The initial phase of the ecological classification and inventory work involved data identification and assembly; the synthesis of data and creation of GIS base maps and graphics; and solicitation of input from local experts on the type and condition of natural resources in the Kansas City metropolitan area. -
Natural Resources Inventory
Natural Resources Inventory Columbia Metropolitan Planning Area Review Draft (10-1-10) NATURAL RESOURCES INVENTORY Review Draft (10-1-10) City of Columbia, Missouri October 1, 2010 - Blank - Preface for Review Document The NRI area covers the Metropolitan Planning Area defined by the Columbia Area Transportation Study Organization (CATSO), which is the local metropolitan planning organization. The information contained in the Natural Resources Inventory document has been compiled from a host of public sources. The primary data focus of the NRI has been on land cover and tree canopy, which are the product of the classification work completed by the University of Missouri Geographic Resource Center using 2007 imagery acquired for this project by the City of Columbia. The NRI uses the area’s watersheds as the geographic basis for the data inventory. Landscape features cataloged include slopes, streams, soils, and vegetation. The impacts of regulations that manage the landscape and natural resources have been cataloged; including the characteristics of the built environment and the relationship to undeveloped property. Planning Level of Detail NRI data is designed to support planning and policy level analysis. Not all the geographic data created for the Natural Resources Inventory can be used for accurate parcel level mapping. The goal is to produce seamless datasets with a spatial quality to support parcel level mapping to apply NRI data to identify the individual property impacts. There are limitations to the data that need to be made clear to avoid misinterpretations. Stormwater Buffers: The buffer data used in the NRI are estimates based upon the stream centerlines, not the high water mark specified in City and County stormwater regulations.