WWF Global 200 Reportfinal
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Russia's Boreal Forests
Forest Area Key Facts & Carbon Emissions Russia’s Boreal Forests from Deforestation Forest location and brief description Russia is home to more than one-fifth of the world’s forest areas (approximately 763.5 million hectares). The Russian landscape is highly diverse, including polar deserts, arctic and sub-arctic tundra, boreal and semi-tundra larch forests, boreal and temperate coniferous forests, temperate broadleaf and mixed forests, forest-steppe and steppe (temperate grasslands, savannahs, and shrub-lands), semi-deserts and deserts. Russian boreal forests (known in Russia as the taiga) represent the largest forested region on Earth (approximately 12 million km2), larger than the Amazon. These forests have relatively few tree species, and are composed mainly of birch, pine, spruce, fir, with some deciduous species. Mixed in among the forests are bogs, fens, marshes, shallow lakes, rivers and wetlands, which hold vast amounts of water. They contain more than 55 per cent of the world’s conifers, and 11 per cent of the world’s biomass. Unique qualities of forest area Russia’s boreal region includes several important Global 200 ecoregions - a science-based global ranking of the Earth’s most biologically outstanding habitats. Among these is the Eastern-Siberian Taiga, which contains the largest expanse of untouched boreal forest in the world. Russia’s largest populations of brown bear, moose, wolf, red fox, reindeer, and wolverine can be found in this region. Bird species include: the Golden eagle, Black- billed capercaillie, Siberian Spruce grouse, Siberian accentor, Great gray owl, and Naumann’s thrush. Russia’s forests are also home to the Siberian tiger and Far Eastern leopard. -
Potential Invasive Plant Expansion in Global Ecoregions Under Climate Change
Potential invasive plant expansion in global ecoregions under climate change Chun-Jing Wang1,2, Qiang-Feng Li2 and Ji-Zhong Wan1 1 State Key Laboratory of Plateau Ecology and Agriculture, Qinghai University, Xining, China 2 College of Agriculture and Animal Husbandry, Qinghai University, Xining, China ABSTRACT Climate change is increasing the risk of invasive plant expansion worldwide. However, few studies have specified the relationship between invasive plant expansion and ecoregions at the global scale under climate change. To address this gap, we provide risk maps highlighting the response of invasive plant species (IPS), with a focus on terrestrial and freshwater ecoregions to climate change, and further explore the climatic features of ecosystems with a high potential for invasive plant expansion under climate change. We use species distribution modelling to predict the suitable habitats of IPS with records at the global scale. Hotspots with a potential risk of IPS (such as aquatic plants, trees, and herbs) expanding in global ecoregions were distributed in Northern Europe, the UK, South America, North America, southwest China, and New Zealand. Temperature changes were related to the potential of IPS expansion in global ecoregions under climate change. Coastal and high latitude ecoregions, such as temperate forests, alpine vegetation, and coastal rivers, were severely infiltrated by IPS under climate change. Monitoring strategies should be defined for climate change for IPS, particularly for aquatic plants, trees, and herbs in the biomes of regions with coastal or high latitudes. The role of climate change on the potential for IPS expansion should be taken into consideration for biological conservation and risk evaluation of IPS at ecoregional scales. -
The Coastal Scrub and Chaparral Bird Conservation Plan
The Coastal Scrub and Chaparral Bird Conservation Plan A Strategy for Protecting and Managing Coastal Scrub and Chaparral Habitats and Associated Birds in California A Project of California Partners in Flight and PRBO Conservation Science The Coastal Scrub and Chaparral Bird Conservation Plan A Strategy for Protecting and Managing Coastal Scrub and Chaparral Habitats and Associated Birds in California Version 2.0 2004 Conservation Plan Authors Grant Ballard, PRBO Conservation Science Mary K. Chase, PRBO Conservation Science Tom Gardali, PRBO Conservation Science Geoffrey R. Geupel, PRBO Conservation Science Tonya Haff, PRBO Conservation Science (Currently at Museum of Natural History Collections, Environmental Studies Dept., University of CA) Aaron Holmes, PRBO Conservation Science Diana Humple, PRBO Conservation Science John C. Lovio, Naval Facilities Engineering Command, U.S. Navy (Currently at TAIC, San Diego) Mike Lynes, PRBO Conservation Science (Currently at Hastings University) Sandy Scoggin, PRBO Conservation Science (Currently at San Francisco Bay Joint Venture) Christopher Solek, Cal Poly Ponoma (Currently at UC Berkeley) Diana Stralberg, PRBO Conservation Science Species Account Authors Completed Accounts Mountain Quail - Kirsten Winter, Cleveland National Forest. Greater Roadrunner - Pete Famolaro, Sweetwater Authority Water District. Coastal Cactus Wren - Laszlo Szijj and Chris Solek, Cal Poly Pomona. Wrentit - Geoff Geupel, Grant Ballard, and Mary K. Chase, PRBO Conservation Science. Gray Vireo - Kirsten Winter, Cleveland National Forest. Black-chinned Sparrow - Kirsten Winter, Cleveland National Forest. Costa's Hummingbird (coastal) - Kirsten Winter, Cleveland National Forest. Sage Sparrow - Barbara A. Carlson, UC-Riverside Reserve System, and Mary K. Chase. California Gnatcatcher - Patrick Mock, URS Consultants (San Diego). Accounts in Progress Rufous-crowned Sparrow - Scott Morrison, The Nature Conservancy (San Diego). -
Impacts of Climate Change on the Worldts Most Exceptional Ecoregions
Impacts of climate change on the world’s most exceptional ecoregions Linda J. Beaumonta,b,1, Andrew Pitmanc, Sarah Perkinsc, Niklaus E. Zimmermannd, Nigel G. Yoccoze, and Wilfried Thuillerb aDepartment of Biological Sciences, Macquarie University, Sydney, NSW 2109, Australia; bLaboratoire d’Ecologie Alpine, Unité Mixte de Recherche Centre National de la Recherche Scientifique 5553, Université de Grenoble, BP 53, 38041 Grenoble Cedex 9, France; cClimate Change Research Centre, University of New South Wales, Sydney, NSW 2052, Australia; dLandscape Dynamics, Swiss Federal Research Institute for Forest, Snow and Landscape Research, 8903 Birmensdorf, Switzerland; and eDepartment of Arctic and Marine Biology, Faculty of Biosciences, Fisheries and Economics, University of Tromsø, N-9037 Tromsø, Norway Edited by Rodolfo Dirzo, Stanford University, Stanford, CA, and approved December 16, 2010 (received for review June 6, 2010) The current rate of warming due to increases in greenhouse gas 200 would be of immense value to conservation efforts worldwide (GHG) emissions is very likely unprecedented over the last 10,000 y. because of their richness in endemic species, high taxonomic Although the majority of countries have adopted the view that uniqueness, unique ecological or evolutionary phenomena, global global warming must be limited to <2 °C, current GHG emission rarity, and their representation of biomes (16). However, the rates and nonagreement at Copenhagen in December 2009 increase majority of these regions are threatened by habitat loss, frag- the likelihood of this limit being exceeded by 2100. Extensive evi- mentation, and degradation, with 147 of 185 terrestrial and fi dence has linked major changes in biological systems to 20th cen- freshwater regions being classi ed as either vulnerable or critically fi tury warming. -
Options for Support to Grassland Restoration in the Context of Climate Change Mitigation
Final Report Options for Support to Grassland Restoration in the context of Climate Change Mitigation Freiburg, Germany, May 2012 Options for Support to Grassland Restoration in the context of Climate Change Mitigation Client: FAO Authors: Andreas Wilkes, Katalin Solymosi, Timm Tennigkeit Content Content .......................................................................................................................................... 3 Key messages ................................................................................................................................ 1 1 Background and perspectives .................................................................................................. 2 1.1 Economic and food security contributions of grassland-based livestock production ..... 3 1.2 Grasslands: an under-prioritized and vulnerable ecosystem ........................................... 5 1.3 Environmental services of grasslands and grassland restoration .................................... 9 1.4 Climate change mitigation potential of grassland protection and restoration.............. 10 1.5 Synergies between grassland protection / restoration and other policy priorities ....... 15 2 Existing grassland protection and restoration initiatives and incentive mechanisms ........... 16 2.1 Incentive mechanisms for grassland protection and restoration .................................. 16 2.2 Other initiatives for grassland protection and restoration ............................................ 19 2.3 Carbon-targeted initiatives -
Conservation Issues: California Chaparral
Author's personal copy Conservation Issues: California Chaparral RW Halsey, California Chaparral Institute, Escondido, CA, United States JE Keeley, U.S. Geological Survey, Three Rivers, CA, United States ã 2016 Elsevier Inc. All rights reserved. What Is Chaparral? 1 California Chaparral Biodiversity 1 Chaparral Community Types 1 Measuring Chaparral Biodiversity 4 Diversity Within Individual Plant Taxa 5 Faunal Diversity 5 Influence of Geology 7 Influence of Climate 7 Influence of Fire 8 Impact of Climate Change 10 Preserving Chaparral Biodiversity 10 References 10 What Is Chaparral? Chaparral is a diverse, sclerophyllous shrub-dominated plant community shaped by a Mediterranean-type climate (hot, dry summers and mild, wet winters), a complex mixture of relatively young soils (Specht and Moll, 1983), and large, infrequent, high-intensity fires (30–150 year fire return interval) (Keeley and Zedler, 2009; Keeley et al., 2004; Lombardo et al., 2009). Large expanses of dense chaparral vegetation cover coastal mesas, canyons, foothills, and mountain slopes throughout the California Floristic Province (Figure 1), southward into Baja California, and extending north into the Rogue River Valley of southwest Oregon. Disjunct patches of chaparral can also be found in central and southeastern Arizona and northern Mexico (Keeley, 2000). Along with the four other Mediterranean-type climate regions of the world with similar shrubland vegetation (Central Chile, Mediterranean Basin, South Africa, and southwestern Australia) (Table 1), California has been designated a biodiversity hot spot (Myers et al., 2000). Twenty-five designated locations in all, these hot spots have exceptional concentrations of endemic species that are undergoing exceptional loss of habitat (Myers et al., 2000; Rundel, 2004). -
Oak Woodlands and Chaparral
Oak Woodlands and Chaparral Aligning chaparral-associated bird needs with oak woodland restoration and fuel reduction in southwest Oregon and northern California Why conservation is needed Oak woodland habitat in southwest Oregon and northern California is comprised of a vegetation gradient that includes oak savanna, open oak woodlands with grass or chaparral understory, closed canopy oak woodlands, and oak conifer forests. Oak habitats are at risk due to development, encroachment of coniferous forest, invasion of exotic species, and lack of oak regeneration. Birds and other wildlife that depend on these ecosystems have been negatively affected by habitat threats. Photo by Jaime Stephens What is chaparral and why is it important for birds? “Chaparral” is a short, shrubby vegetation type that can be composed of a variety of plant species. In this region, chaparral habitat is often associated with oak woodlands. Chaparral is a natural part of oak habitats, but it also poses a risk of spreading severe fire which can put large, old oak trees at risk. Because oak woodlands are threatened by loss and degradation, management initiatives sometimes reduce chaparral to reduce the risk of high severity fire and promote a mix of low to moderate severity fire. Still, functioning oak woodland mosaics in southern Oregon need many types of vegetation cover, including patches of chaparral. Restoring and managing oak woodland ecosystems in this region requires learning how to best achieve a balanced vegetation composition that includes chaparral habitat components. KBO, in partnership with the Klamath Siskiyou Oak Network, has conducted studies to determine how we might best manage oak and chaparral habitat for bird species. -
The Chaparral Vegetation in Mexico Under Nonmediterranean Climate: the Convergence and Madrean-Tethyan Hypotheses Reconsidered1
American Journal of Botany 85(10): 1398±1408. 1998. THE CHAPARRAL VEGETATION IN MEXICO UNDER NONMEDITERRANEAN CLIMATE: THE CONVERGENCE AND MADREAN-TETHYAN HYPOTHESES RECONSIDERED1 ALFONSO VALIENTE-BANUET,2,4 NOEÂ FLORES-HERNAÂ NDEZ,2 MIGUEL VERDUÂ ,3 AND PATRICIA DAÂ VILA3 2Instituto de EcologõÂa, Universidad Nacional AutoÂnoma de MeÂxico, Apartado Postal 70±275, UNAM, 04510 MeÂxico, D.F.; and 3UBIPRO, ENEP-Iztacala, Universidad Nacional AutoÂnoma de MeÂxico, Apartado Postal 314, MeÂxico, 54090, Tlalnepantla, MeÂxico A comparative study between an unburned evergreen sclerophyllous vegetation located in south-central Mexico under a wet-summer climate, with mediterranean regions was conducted in order to re-analyze vegetation and plant characters claimed to converge under mediterranean climates. The comparison considered ¯oristic composition, plant-community struc- ture, and plant characters as adaptations to mediterranean climates and analyzed them by means of a correspondence analysis, considering a tropical spiny shrubland as the external group. We made a species register of the number of species that resprouted after a ®re occurred in 1995 and a distribution map of the evergreen sclerophyllous vegetation in Mexico (mexical) under nonmediterranean climates. The TehuacaÂn mexical does not differ from the evergreen sclerophyllous areas of Chile, California, Australia, and the Mediterranean Basin, according to a correspondence analysis, which ordinated the TehuacaÂn mexical closer to the mediter- ranean areas than to the external group. All the vegetation and ¯oristic characteristics of the mexical, as well as its distribution along the rain-shadowed mountain parts of Mexico, support its origin in the Madrean-Tethyan hypothesis of Axelrod. Therefore, these results allow to expand the convergence paradigm of the chaparral under an integrative view, in which a general trend to aridity might explain ¯oristic and adaptive patterns detected in these environments. -
A Global Overview of Wetland and Marine Protected Areas on the World Heritage List
A GLOBAL OVERVIEW OF WETLAND AND MARINE PROTECTED AREAS ON THE WORLD HERITAGE LIST A Contribution to the Global Theme Study of World Heritage Natural Sites Prepared by Jim Thorsell, Renee Ferster Levy and Todd Sigaty Natural Heritage Programme lUCN Gland, Switzerland September 1997 WORLD CONSERVATION MONITORING CENTRE lUCN The World Conservation Union 530S2__ A GLOBAL OVERVIEW OF WETLAND AND MARINE PROTECTED AREAS ON THE WORLD HERITAGE LIST A Contribution to the Global Theme Study of Wodd Heritage Natural Sites Prepared by Jim Thorsell. Renee Ferster Levy and Todd Sigaty Natural Heritage Program lUCN Gland. Switzerland September 1997 Working Paper 1: Earth's Geological History - A Contextual Framework Assessment of World Heritage Fossil Site Nominations Working Paper 2: A Global Overview of Wetland and Marine Protected Areas on the World Heritage List Working Paper 3; A Global Overview of Forest Protected Areas on the World Heritage List Further volumes (in preparation) on biodiversity, mountains, deserts and grasslands, and geological features. Digitized by tine Internet Arciiive in 2010 witii funding from UNEP-WCIVIC, Cambridge littp://www.arcliive.org/details/globaloverviewof97glob . 31 TABLE OF CONTE>rrS PAGE I. Executive Summary (e/f) II. Introduction 1 III. Tables & Figures Table 1 . Natural World Heritage sites with primary wetland and marine values 1 Table 2. Natural World Heritage sites with secondary wetland and marine values 12 Table 3. Natural World Heritage sites inscribed primarily for their freshwater wetland values 1 Table 4. Additional natural World Heritage sites with significant freshwater wetland values 14 Tables. Natural World Heritage sites with a coastal/marine component 15 Table 6. -
Biodiversity and Management of the Madrean Archipelago
)I This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. A Classification System and Map of the Biotic Communities of North America David E. Brown, Frank Reichenbacher, and Susan E. Franson 1 Abstract.-Biotic communities (biomes) are regional plant and animal associations within recognizable zoogeographic and floristic provinces. Using the previous works and modified terminology of biologists, ecologists, and biogeographers, we have developed an hierarchical classification system for the world's biotic communities. In use by the Arid Ecosystems Resource Group of the Environmental Protection Agency's Environmental Monitoring and Assessment Program, the Arizona Game and Fish Department, and other Southwest agencies, this classification system is formulated on the limiting effects of moisture and temperature minima on the structure and composition of vegetation while recognizing specific plant and animal adaptations to regional environments. To illustrate the applicability of the classification system, the Environmental Protection Agency has funded the preparation of a 1: 10,000,000 color map depicting the major upland biotic communities of North America using an ecological color scheme that shows gradients in available plant moisture, heat, and cold. Digitized and computer compatible, this hierarchical system facilitates biotic inventory and assessment, the delineation and stratification of habitats, and the identification of natural areas in need of acquisition, Moreover, the various categories of the classification are statistically testable through the use of existing climatic data, and analysis of plant and animal distributions. Both the classification system and map are therefore of potential use to those interested in preserving biotic diversity. -
Endemic Family
Endemic family Lomolino et al., 2006 Biogeography 1 Prof. J. Hicke Endemic species Lomolino et al., 2006 Biogeography 2 Prof. J. Hicke Cosmopolitan family Lomolino et al., 2006 Biogeography 3 Prof. J. Hicke Cosmopolitan species www.peregrinefund.org/explore_raptors/ Biogeography 4 Prof. J. Hicke Biogeographic boundaries Biogeography 5 Prof. J. Hicke What’s an angiosperm? Plants gymnosperms angiosperms en.wikipedia.org/wiki Biogeography 6 Prof. J. Hicke Rise of Angiosperms Biogeography 7 Prof. J. Hicke Distribution of pines and southern beeches Long dispersal distances, ocean barriers prevented cold-adapted angiosperms to colonize Northern Hemisphere high latitudes 100 pine species, only several southern beech species (unusual) Biogeography 8 Prof. J. Hicke Biogeographic realms Biogeography 9 Prof. J. Hicke Nearctic/Palearctic Regions • Two regions have similar mammals, angiosperms • similar environmental conditions • physical connections leading to substantial exchange • Mammal fauna smaller than that of tropics • 13 families of terrestrial mammals in Nearctic • 18 in Palearctic • Dominated by placentals (none in Palearctic, one in Nearctic) • More species during Pleistocene than today • Cooling and glaciation in Pleistocene produced cold-adapted mammals; cycles caused extinctions Biogeography 10 Prof. J. Hicke Neotropical Region • Mammals: 23 families • many families shared with Nearctic (e.g., foxes, rabbits, mountain lions) • New World monkeys • 3 families, 84 species of marsupials • Angiosperms: most diverse region (137 families, 50 endemic) • shared families with other regions • High biodiversity: • environmental variety: tundra, temperate and tropical forests, desert • geologic history: early connections with Africa, Antarctica; exchange with Nearctic Biogeography 11 Prof. J. Hicke Ethiopian Region • Has most diverse mammal fauna: 30 families • charismatic megafauna • some families shared with Palearctic, Oriental • later collision with Eurasia • few/none shared with Neotropical, Australasian • early separation from S. -
Climate Zones and Biomes
Geography Climate Zones and Biomes Pupil Workbook Year 3, Unit 4 Name: Formative Assessment Scores Knowledge Quiz 4.1 Knowledge Quiz 4.4 Knowledge Quiz 4.2 Knowledge Quiz 4.5 Knowledge Quiz 4.3 Notes: Geography Climate Zones and Biomes Pupil Workbook Year 3, Unit 4 Climate Zones and Biomes Knowledge Organiser Vocabulary Biome Definition The weather conditions in an area 1 Climate 8 Rainforest A thick forest that has a lot of rain over time A grassy plain in tropical and An area with similar plants and 9 Savannah 2 Biome subtropical regions with definition animals A waterless area with little or 10 Desert Smaller regions indicating where no vegetation 3 Vegetation belt vegetation grows An area that has mainly shrubs and 11 Chaparral Polar and Areas in the north and south of thorny bushes 4 subpolar zone the globe A large open area covered with 12 Grassland grass 5 Temperate zone Areas of mild temperature Deciduous A forest that has trees that lose 13 forest their leaves each year Equatorial and Area in the centre of the globe with 6 A forest made up of coniferous Tropical zones a hot temperature 14 Boreal forest plants in cold areas 7 Arid zone Areas north and south of the tropics 15 Tundra A flat, cold, treeless area Climate Equatorial zone Tropical zone Arid zone Mediterranean zone Temperate zone Subpolar zone Polar zone Biomes Polar Desert Tundra Boreal forest Tropical Rainforest Deciduous forest Grassland Savannah Desert Chaparral Challenges of a biome for humans Biomes in Europe Rainforest: Grassland • It can rain more than 250cm a