SPOTLIGHT Biomes
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Arachnozoogeographical Analysis of the Boundary Between Eastern Palearctic and Indomalayan Region
Historia naturalis bulgarica, 23: 5-36, 2016 Arachnozoogeographical analysis of the boundary between Eastern Palearctic and Indomalayan Region Petar Beron Abstract: This study aims to test how the distribution of various orders of Arachnida follows the classical subdivision of Asia and where the transitional zone between the Eastern Palearctic (Holarctic Kingdom) and the Indomalayan Region (Paleotropic) is situated. This boundary includes Thar Desert, Karakorum, Himalaya, a band in Central China, the line north of Taiwan and the Ryukyu Islands. The conclusion is that most families of Arachnida (90), excluding most of the representatives of Acari, are common for the Palearctic and Indomalayan Regions. There are no endemic orders or suborders in any of them. Regarding Arach- nida, their distribution does not justify the sharp difference between the two Kingdoms (Paleotropical and Holarctic) in Eastern Eurasia. The transitional zone (Sino-Japanese Realm) of Holt et al. (2013) also does not satisfy the criteria for outlining an area on the same footing as the Palearctic and Indomalayan Realms. Key words: Palearctic, Indomalayan, Arachnozoogeography, Arachnida According to the classical subdivision the region’s high mountains and plateaus. In southern Indomalayan Region is formed from the regions in Asia the boundary of the Palearctic is largely alti- Asia that are south of the Himalaya, and a zone in tudinal. The foothills of the Himalaya with average China. North of this “line” is the Palearctic (consist- altitude between about 2000 – 2500 m a.s.l. form the ing og different subregions). This “line” (transitional boundary between the Palearctic and Indomalaya zone) is separating two kingdoms, therefore the dif- Ecoregions. -
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 -
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. -
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. -
Sanderson Et Al., the Human Footprint and the Last of the Wild
Articles The Human Footprint and the Last of the Wild ERICW. SANDERSON,MALANDING JAITEH, MARC A. LEVY,KENT H. REDFORD, ANTOINETTEV. WANNEBO,AND GILLIANWOOLMER n Genesis,God blesses humanbeings and bids us to take dominion over the fish in the sea,the birdsin the air, THE HUMANFOOTPRINT IS A GLOBAL and other We are entreatedto be fruitful every living thing. MAPOF HUMANINFLUENCE ON THE and multiply,to fill the earth,and subdueit (Gen. 1:28).The bad news, and the good news, is that we have almost suc- LANDSURFACE, WHICH SUGGESTSTHAT ceeded. Thereis little debatein scientificcircles about the impor- HUMANBEINGS ARE STEWARDS OF tance of human influenceon ecosystems.According to sci- WE LIKEIT OR NOT entists'reports, we appropriateover 40%of the net primary NATURE,WHETHER productivity(the greenmaterial) produced on Eartheach year (Vitouseket al. 1986,Rojstaczer et al.2001). We consume 35% thislack of appreciationmay be dueto scientists'propensity of the productivityof the oceanicshelf (Pauly and Christensen to expressthemselves in termslike "appropriation of net pri- 1995), and we use 60% of freshwaterrun-off (Postel et al. maryproductivity" or "exponentialpopulation growth," ab- 1996). The unprecedentedescalation in both human popu- stractionsthat require some training to understand.It may lation and consumption in the 20th centuryhas resultedin be dueto historicalassumptions about and habits inherited environmentalcrises never before encountered in the history fromtimes when human beings, as a group,had dramatically of humankindand the world (McNeill2000). E. O. Wilson less influenceon the biosphere.Now the individualdeci- (2002) claims it would now take four Earthsto meet the consumptiondemands of the currenthuman population,if Eric Sanderson(e-mail: [email protected])is associatedirector, and every human consumed at the level of the averageUS in- W. -
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). -
North Yukon Planning Region Biophysical Landscape Classification
North Yukon Planning Region Biophysical Landscape Classification (Landscape Types): Overview, Methods and Reference Images T F DRA Updated October 20, 2005 Project Team • John Meikle, Yukon Environment • Marcus Waterreus, Yukon Environment • Shawn Francis, NYPC • Jeff Hamm, YLUPC • Nancy Steffen, GLL • Biophysical working group – initial terrain and bioclimate concepts STUDY AREA • North Yukon Planning Region (55,000 km2) • Taiga Cordillera Ecozone • 6 Ecoregions: Eagle Plains, Old Crow Flats, Old Crow Basin, North Ogilvie Mountains, Davidson Mountains, Richardson Mountains • Basin, Plateau and Mountain Landscapes STUDY AREA Physiographic Basin Units and Ecodistricts Mountain Basin Plateau Old Crow Plateau Mountain Mountain MAPPING CONCEPTS • Mountain landscapes organized by elevation (Bioclimate Zone); Plateau landscapes organized by relative moisture gradient (Ecosite) • Beyond major Basin landscapes, surficial materials not controlling factor (unglaciated) • Mapping has regional applications (1:100K- 1:250K) • Available data sources are major determinant of potential methods DATA INPUTS • EOSD (25m LANDSAT Extent of 250K Regional Terrain supervised classification) Map (raster) • 90m DEM (raster) • 250K regional terrain map North Yukon Planning Region (vector) Peel Watershed …..due to importance of Planning Region EOSD and DEM, raster mapping approach was chosen METHODS • Field reconnaissance; develop concepts • Create regional terrain and Bioclimate Zone map through manual interpretation (refine Ecoregions and Ecodistricts to 250K) -
Responses of Plant Communities to Grazing in the Southwestern United States Department of Agriculture United States Forest Service
Responses of Plant Communities to Grazing in the Southwestern United States Department of Agriculture United States Forest Service Rocky Mountain Research Station Daniel G. Milchunas General Technical Report RMRS-GTR-169 April 2006 Milchunas, Daniel G. 2006. Responses of plant communities to grazing in the southwestern United States. Gen. Tech. Rep. RMRS-GTR-169. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 126 p. Abstract Grazing by wild and domestic mammals can have small to large effects on plant communities, depend- ing on characteristics of the particular community and of the type and intensity of grazing. The broad objective of this report was to extensively review literature on the effects of grazing on 25 plant commu- nities of the southwestern U.S. in terms of plant species composition, aboveground primary productiv- ity, and root and soil attributes. Livestock grazing management and grazing systems are assessed, as are effects of small and large native mammals and feral species, when data are available. Emphasis is placed on the evolutionary history of grazing and productivity of the particular communities as deter- minants of response. After reviewing available studies for each community type, we compare changes in species composition with grazing among community types. Comparisons are also made between southwestern communities with a relatively short history of grazing and communities of the adjacent Great Plains with a long evolutionary history of grazing. Evidence for grazing as a factor in shifts from grasslands to shrublands is considered. An appendix outlines a new community classification system, which is followed in describing grazing impacts in prior sections. -
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. -
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). -
The Ecology of Large Herbivores Native to the Coastal Lowlands of the Fynbos Biome in the Western Cape, South Africa
The ecology of large herbivores native to the coastal lowlands of the Fynbos Biome in the Western Cape, South Africa by Frans Gustav Theodor Radloff Dissertation presented for the degree of Doctor of Science (Botany) at Stellenbosh University Promoter: Prof. L. Mucina Co-Promoter: Prof. W. J. Bond December 2008 DECLARATION By submitting this dissertation electronically, I declare that the entirety of the work contained therein is my own, original work, that I am the owner of the copyright thereof (unless to the extent explicitly otherwise stated) and that I have not previously in its entirety or in part submitted it for obtaining any qualification. Date: 24 November 2008 Copyright © 2008 Stellenbosch University All rights reserved ii ABSTRACT The south-western Cape is a unique region of southern Africa with regards to generally low soil nutrient status, winter rainfall and unusually species-rich temperate vegetation. This region supported a diverse large herbivore (> 20 kg) assemblage at the time of permanent European settlement (1652). The lowlands to the west and east of the Kogelberg supported populations of African elephant, black rhino, hippopotamus, eland, Cape mountain and plain zebra, ostrich, red hartebeest, and grey rhebuck. The eastern lowlands also supported three additional ruminant grazer species - the African buffalo, bontebok, and blue antelope. The fate of these herbivores changed rapidly after European settlement. Today the few remaining species are restricted to a few reserves scattered across the lowlands. This is, however, changing with a rapid growth in the wildlife industry that is accompanied by the reintroduction of wild animals into endangered and fragmented lowland areas. -
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.