The Responses of Tropical Forest Species to Global Cli‐ Mate Change: Acclimate, Adapt, Migrate Or Go Ex‐ Tinct? Kenneth J
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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 -
The Eastern Africa Coastal Forests Ecoregion
The Eastern Africa Coastal Forests Ecoregion Strategic Framework for Conservation 2005 – 2025 Strategic Framework for Conservation (2005–2025) The Eastern Afrca Coastal Forests Ecoregon Strategc Framework for Conservaton 2005–2025 The Eastern Africa Coastal Forests Ecoregion Publshed August 2006 Editor: Kimunya Mugo Design and layout: Anthony Mwangi Cover design: Kimunya Mugo Front cover main photo: WWF-EARPO / John SALEHE Front cover other photos: WWF-UK / Brent STIRTON / Getty Images Back cover photo: WWF-EARPO / John SALEHE Photos: John Salehe, David Maingi and Neil Burgess or as credited. © Graphics (2006) WWF-EARPO. All rights reserved. The material and geographic designations in this report do not imply the expression of any opinion whatsoever on the part of WWF concerning the legal status of any country, territory or area or concerning the delimitation of its frontiers and boundaries. WWF Eastern Africa Regional Programme Office ACS Plaza, Lenana Road P.O. Box 62440-00200 Nairobi, Kenya Tel: +254 20 3877355, 3872630/1 Fax: +254 20 3877389 E-mail: [email protected] Web: www.panda.org/earpo Strategic Framework for Conservation (2005–2025) Contents Acknowledgements......................................................................................................... iv Foreword........................................................................................................................... v Lst of abbrevatons and acronyms.............................................................................. v A new approach to -
Grasslands 4/16/03 3:46 PM
Ecoregion: Grasslands 4/16/03 3:46 PM Grasslands INTRODUCTION About 25% of Earth’s land surface is covered by temperate grassland. These large expanses of flat or hilly country cover much of North America, as well as large areas of Europe, Asia, and South America. Most grasslands are found in the interiors of continents, where there is too little rainfall for a forest but too much rain for a desert. Art Explosion Art Explosion Rolling hills covered with grasses and very few trees A few scattered trees are found on savannas, are typical of North American grassland prairies. tropical grasslands of Africa. Temperate grasslands have subtle differences and different names throughout the world. Prairies and plains of North America are grasslands with tall grasses, while the steppes of Russia are grasslands with short grasses. Veldts are found in South Africa, the puszta in Hungary, and the pampas in Argentina and Uruguay. Savannas are tropical grasslands that support scattered trees and shrubs. They often form a transitional biome file:///Ecoregion/grass/content.html Page 1 of 6 Ecoregion: Grasslands 4/16/03 3:46 PM between deserts and rain forests. Some temperate grasslands are also called savannas. The word savanna comes from the Spanish word zavanna, meaning “treeless plain.” Savannas cover almost half of Africa (mostly central Africa) and large areas of Australia and South America. ABIOTIC DATA The grassland climate is rather dry, averaging about 20 to 100 centimeters (8–40 inches) of precipitation a year. Summers are very hot and may reach 45°C (113°F). Winter temperatures often fall below freezing, which is 0°C (32°F). -
Fact Sheet- Central California Coast Ecoregion
California State Wildlife Action Plan (SWAP) 2015 Central California Coast Region Annual and Perennial Grassland Habitat About Our Region and the Grassland Habitat Annual grassland habitats are open grasslands composed primarily of annual plant species such as introduced annual grasses and forbs. Annual grasslands also occur as understory plants in Valley Oak Woodland and other habitats. Perennial grassland habitats occur as coastal prairie and interspersed within annual grasslands. Vernal pools also are an important habitat component of many grassland systems. The structure of grasslands depends upon prevailing weather patterns and grazing. A number of wildlife species spend their entire life within grasslands while others use grasslands for foraging and breeding. What are the sensitive species found in the grassland habitat? The following 32 grassland dependent species from this region are found to be sensitive: Amphibian [3] CALIFORNIA TIGER SALAMANDER WESTERN SPADEFOOT RED-LEGGED FROG Reptile [1] BLUNT-NOSED LEOPARD LIZARD Bird [15] BURROWING OWL NORTHERN HARRIER CALIFORNIA CONDOR OREGON VESPER SPARROW GIANT KANGAROO RAT PURPLE MARTIN GRASSHOPPER SPARROW SAND-HILL CRANE GOLDEN EAGLE SHORT-EARED OWL LOGGERHEAD SHRIKE SWAINSON’S HAWK LONG-BILLED CURLEW TRICOLORED BLACKBIRD MOUNTAIN PLOVER Mammal [13] BIG FREE-TAILED BAT PALLID SAN DIEGO POCKET MOUSE CALIFORNIA LEAF-NOSED BAT POCKETED FREE-TAILED BATRINGTAIL HOARY BAT SOUTHERN GRASSHOPPER MOUSE JACUMBA POCKET MOUSE SAN JOAQUIN KIT FOX LONG-EARED MYOTIS TOWNSEND BIG- EARED BAT MAINLAND -
Characterization of Ecoregions of Idaho
1 0 . C o l u m b i a P l a t e a u 1 3 . C e n t r a l B a s i n a n d R a n g e Ecoregion 10 is an arid grassland and sagebrush steppe that is surrounded by moister, predominantly forested, mountainous ecoregions. It is Ecoregion 13 is internally-drained and composed of north-trending, fault-block ranges and intervening, drier basins. It is vast and includes parts underlain by thick basalt. In the east, where precipitation is greater, deep loess soils have been extensively cultivated for wheat. of Nevada, Utah, California, and Idaho. In Idaho, sagebrush grassland, saltbush–greasewood, mountain brush, and woodland occur; forests are absent unlike in the cooler, wetter, more rugged Ecoregion 19. Grazing is widespread. Cropland is less common than in Ecoregions 12 and 80. Ecoregions of Idaho The unforested hills and plateaus of the Dissected Loess Uplands ecoregion are cut by the canyons of Ecoregion 10l and are disjunct. 10f Pure grasslands dominate lower elevations. Mountain brush grows on higher, moister sites. Grazing and farming have eliminated The arid Shadscale-Dominated Saline Basins ecoregion is nearly flat, internally-drained, and has light-colored alkaline soils that are Ecoregions denote areas of general similarity in ecosystems and in the type, quality, and America into 15 ecological regions. Level II divides the continent into 52 regions Literature Cited: much of the original plant cover. Nevertheless, Ecoregion 10f is not as suited to farming as Ecoregions 10h and 10j because it has thinner soils. -
The Impacts of Increasing Drought on Forest Dynamics, Structure, and Biodiversity in the United States
Global Change Biology (2016) 22, 2329–2352, doi: 10.1111/gcb.13160 SPECIAL FEATURE The impacts of increasing drought on forest dynamics, structure, and biodiversity in the United States JAMES S. CLARK1 , LOUIS IVERSON2 , CHRISTOPHER W. WOODALL3 ,CRAIGD.ALLEN4 , DAVID M. BELL5 , DON C. BRAGG6 , ANTHONY W. D’AMATO7 ,FRANKW.DAVIS8 , MICHELLE H. HERSH9 , INES IBANEZ10, STEPHEN T. JACKSON11, STEPHEN MATTHEWS12, NEIL PEDERSON13, MATTHEW PETERS14,MARKW.SCHWARTZ15, KRISTEN M. WARING16 andNIKLAUS E. ZIMMERMANN17 1Nicholas School of the Environment, Duke University, Durham, NC 27708, USA, 2Forest Service, Northern Research Station 359 Main Road, Delaware, OH 43015, USA, 3Forest Service 1992 Folwell Avenue,Saint Paul, MN 55108, USA, 4U.S. Geological Survey, Fort Collins Science Center Jemez Mountains Field Station, Los Alamos, NM 87544, USA, 5Forest Service, Pacific Northwest Research Station, Corvallis, OR 97331, USA, 6Forest Service, Southern Research Station, Monticello, AR 71656, USA, 7Rubenstein School of Environment and Natural Resources, University of Vermont, 04E Aiken Center, 81 Carrigan Dr., Burlington, VT 05405, USA, 8Bren School of Environmental Science and Management, University of California, Santa Barbara, CA 93106, USA, 9Department of Biology, Sarah Lawrence College, New York, NY 10708, USA, 10School of Natural Resources and Environment, University of Michigan, 2546 Dana Building, Ann Arbor, MI 48109, USA, 11U.S. Geological Survey, Southwest Climate Science Center and Department of Geosciences, University of Arizona, 1064 E. Lowell -
Taiga Plains
ECOLOGICAL REGIONS OF THE NORTHWEST TERRITORIES Taiga Plains Ecosystem Classification Group Department of Environment and Natural Resources Government of the Northwest Territories Revised 2009 ECOLOGICAL REGIONS OF THE NORTHWEST TERRITORIES TAIGA PLAINS This report may be cited as: Ecosystem Classification Group. 2007 (rev. 2009). Ecological Regions of the Northwest Territories – Taiga Plains. Department of Environment and Natural Resources, Government of the Northwest Territories, Yellowknife, NT, Canada. viii + 173 pp. + folded insert map. ISBN 0-7708-0161-7 Web Site: http://www.enr.gov.nt.ca/index.html For more information contact: Department of Environment and Natural Resources P.O. Box 1320 Yellowknife, NT X1A 2L9 Phone: (867) 920-8064 Fax: (867) 873-0293 About the cover: The small photographs in the inset boxes are enlarged with captions on pages 22 (Taiga Plains High Subarctic (HS) Ecoregion), 52 (Taiga Plains Low Subarctic (LS) Ecoregion), 82 (Taiga Plains High Boreal (HB) Ecoregion), and 96 (Taiga Plains Mid-Boreal (MB) Ecoregion). Aerial photographs: Dave Downing (Timberline Natural Resource Group). Ground photographs and photograph of cloudberry: Bob Decker (Government of the Northwest Territories). Other plant photographs: Christian Bucher. Members of the Ecosystem Classification Group Dave Downing Ecologist, Timberline Natural Resource Group, Edmonton, Alberta. Bob Decker Forest Ecologist, Forest Management Division, Department of Environment and Natural Resources, Government of the Northwest Territories, Hay River, Northwest Territories. Bas Oosenbrug Habitat Conservation Biologist, Wildlife Division, Department of Environment and Natural Resources, Government of the Northwest Territories, Yellowknife, Northwest Territories. Charles Tarnocai Research Scientist, Agriculture and Agri-Food Canada, Ottawa, Ontario. Tom Chowns Environmental Consultant, Powassan, Ontario. Chris Hampel Geographic Information System Specialist/Resource Analyst, Timberline Natural Resource Group, Edmonton, Alberta. -
Ecoregions of the Mississippi Alluvial Plain
92° 91° 90° 89° 88° Ecoregions of the Mississippi Alluvial Plain Cape Girardeau 73cc 72 io Ri Ecoregions denote areas of general similarity in ecosystems and in the type, quality, and quantity of This level III and IV ecoregion map was compiled at a scale of 1:250,000 and depicts revisions and Literature Cited: PRINCIPAL AUTHORS: Shannen S. Chapman (Dynamac Corporation), Oh ver environmental resources; they are designed to serve as a spatial framework for the research, subdivisions of earlier level III ecoregions that were originally compiled at a smaller scale (USEPA Bailey, R.G., Avers, P.E., King, T., and McNab, W.H., eds., 1994, Omernik, J.M., 1987, Ecoregions of the conterminous United States (map Barbara A. Kleiss (USACE, ERDC -Waterways Experiment Station), James M. ILLINOIS assessment, management, and monitoring of ecosystems and ecosystem components. By recognizing 2003, Omernik, 1987). This poster is part of a collaborative effort primarily between USEPA Region Ecoregions and subregions of the United States (map) (supplementary supplement): Annals of the Association of American Geographers, v. 77, no. 1, Omernik, (USEPA, retired), Thomas L. Foti (Arkansas Natural Heritage p. 118-125, scale 1:7,500,000. 71 the spatial differences in the capacities and potentials of ecosystems, ecoregions stratify the VII, USEPA National Health and Environmental Effects Research Laboratory (Corvallis, Oregon), table of map unit descriptions compiled and edited by McNab, W.H., and Commission), and Elizabeth O. Murray (Arkansas Multi-Agency Wetland Bailey, R.G.): Washington, D.C., U.S. Department of Agriculture - Forest Planning Team). 37° environment by its probable response to disturbance (Bryce and others, 1999). -
Predicting Future Mangrove Forest Migration in the Everglades Under Rising Sea Level
Predicting Future Mangrove Forest Migration in the Everglades Under Rising Sea Level Mangroves in the Everglades punctuate the vulnerability of mangrove ha) on an annual basis for the entire simu- forests to rising sea level and other climate lated landscape. Each land unit is defined Mangroves are highly productive changes. Global climate change has been by habitat type (forest, marsh, aquatic), ecosystems that provide valued habitat for projected to increase seawater tempera- land elevation, water level, and salinity fish and shorebirds. Mangrove forests are tures and accelerate the rise in sea level conditions. SELVA also calculates prob- universally composed of relatively few which may further compound ecosystem ability functions of disturbance for each tree species and a single overstory strata. stress in mangrove-dominated systems. forest unit relative to potential sea-level Three species of true mangroves are com- These forests are subject to coastal and rise, lightning, and hurricane strikes. In- mon to intertidal zones of the Caribbean inland processes of hydrology largely tertidal forest units are then simulated with and Gulf of Mexico Coast, namely, black controlled by regional climate, disturbance the MANGRO model based on unique sets mangrove (Avicennia germinans), white regimes, and human decisions about water of environmental factors and forest history. mangrove (Laguncularia racemosa), and management. MANGRO is a spatially explicit red mangrove (Rhizophora mangle). Man- Mangroves are halophytes, mean- stand simulation model constructed for grove forests occupy intertidal settings of ing they can tolerate the added stress of mangrove forests of the Neotropics (fig. the coastal margin of the Everglades along waterlogging and salinity conditions that 2). -
Neotropical Rainforest Restoration: Comparing Passive, Plantation and Nucleation Approaches
UC Riverside UC Riverside Previously Published Works Title Neotropical rainforest restoration: comparing passive, plantation and nucleation approaches Permalink https://escholarship.org/uc/item/4hf3v06s Journal BIODIVERSITY AND CONSERVATION, 25(11) ISSN 0960-3115 Authors Bechara, Fernando C Dickens, Sara Jo Farrer, Emily C et al. Publication Date 2016-10-01 DOI 10.1007/s10531-016-1186-7 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Biodivers Conserv DOI 10.1007/s10531-016-1186-7 REVIEW PAPER Neotropical rainforest restoration: comparing passive, plantation and nucleation approaches 1,2 2 2 Fernando C. Bechara • Sara Jo Dickens • Emily C. Farrer • 2,3 2 2,4 Loralee Larios • Erica N. Spotswood • Pierre Mariotte • Katharine N. Suding2,5 Received: 17 April 2016 / Revised: 5 June 2016 / Accepted: 25 July 2016 Ó Springer Science+Business Media Dordrecht 2016 Abstract Neotropical rainforests are global biodiversity hotspots and are challenging to restore. A core part of this challenge is the very long recovery trajectory of the system: recovery of structure can take 20–190 years, species composition 60–500 years, and reestablishment of rare/endemic species thousands of years. Passive recovery may be fraught with instances of arrested succession, disclimax or emergence of novel ecosystems. In these cases, active restoration methods are essential to speed recovery and set a desired restoration trajectory. Tree plantation is the most common active approach to reestablish a high density of native tree species and facilitate understory regeneration. While this approach may speed the successional trajectory, it may not achieve, and possibly inhibit, a long-term restoration trajectory towards the high species diversity characteristic of these forests. -
Description of the Ecoregions of the United States
(iii) ~ Agrl~:::~~;~":,c ullur. Description of the ~:::;. Ecoregions of the ==-'Number 1391 United States •• .~ • /..';;\:?;;.. \ United State. (;lAn) Department of Description of the .~ Agriculture Forest Ecoregions of the Service October United States 1980 Compiled by Robert G. Bailey Formerly Regional geographer, Intermountain Region; currently geographer, Rocky Mountain Forest and Range Experiment Station Prepared in cooperation with U.S. Fish and Wildlife Service and originally published as an unnumbered publication by the Intermountain Region, USDA Forest Service, Ogden, Utah In April 1979, the Agency leaders of the Bureau of Land Manage ment, Forest Service, Fish and Wildlife Service, Geological Survey, and Soil Conservation Service endorsed the concept of a national classification system developed by the Resources Evaluation Tech niques Program at the Rocky Mountain Forest and Range Experiment Station, to be used for renewable resources evaluation. The classifica tion system consists of four components (vegetation, soil, landform, and water), a proposed procedure for integrating the components into ecological response units, and a programmed procedure for integrating the ecological response units into ecosystem associations. The classification system described here is the result of literature synthesis and limited field testing and evaluation. It presents one procedure for defining, describing, and displaying ecosystems with respect to geographical distribution. The system and others are undergoing rigorous evaluation to determine the most appropriate procedure for defining and describing ecosystem associations. Bailey, Robert G. 1980. Description of the ecoregions of the United States. U. S. Department of Agriculture, Miscellaneous Publication No. 1391, 77 pp. This publication briefly describes and illustrates the Nation's ecosystem regions as shown in the 1976 map, "Ecoregions of the United States." A copy of this map, described in the Introduction, can be found between the last page and the back cover of this publication. -
Forest--Savanna Transition Zones
Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Biogeosciences Discuss., 11, 4591–4636, 2014 Open Access www.biogeosciences-discuss.net/11/4591/2014/ Biogeosciences BGD doi:10.5194/bgd-11-4591-2014 Discussions © Author(s) 2014. CC Attribution 3.0 License. 11, 4591–4636, 2014 This discussion paper is/has been under review for the journal Biogeosciences (BG). Forest–savanna Please refer to the corresponding final paper in BG if available. transition zones Structural, physiognomic and E. M. Veenendaal et al. aboveground biomass variation in Title Page savanna-forest transition zones on three Abstract Introduction continents. How different are Conclusions References co-occurring savanna and forest Tables Figures formations? J I E. M. Veenendaal1, M. Torello-Raventos2, T. R. Feldpausch3, T. F. Domingues4, J I 5 3 2,25 3,6 7 8 F. Gerard , F. Schrodt , G. Saiz , C. A. Quesada , G. Djagbletey , A. Ford , Back Close J. Kemp9, B. S. Marimon10, B. H. Marimon-Junior10, E. Lenza10, J. A. Ratter11, L. Maracahipes10, D. Sasaki12, B. Sonké13, L. Zapfack13, D. Villarroel14, Full Screen / Esc M. Schwarz15, F. Yoko Ishida6,16, M. Gilpin3, G. B. Nardoto17, K. Affum-Baffoe18, L. Arroyo14, K. Bloomfield3, G. Ceca1, H. Compaore19, K. Davies2, A. Diallo20, Printer-friendly Version N. M. Fyllas3, J. Gignoux21, F. Hien20, M. Johnson3, E. Mougin22, P. Hiernaux22, Interactive Discussion T. Killeen14,23, D. Metcalfe8, H. S. Miranda17, M. Steininger24, K. Sykora1, M. I. Bird2, J. Grace4, S. Lewis3,26, O. L. Phillips3, and J. Lloyd16,27 4591