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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. -
Desertification and Deforestation in Africa - R
LAND USE, LAND COVER AND SOIL SCIENCES – Vol. V – Desertification and Deforestation in Africa - R. Penny DESERTIFICATION AND DEFORESTATION IN AFRICA R. Penny Environmental and Developmental Consultant/Practitioner, Cape Town, South Africa Keywords: arid, semi-arid, dry sub-humid, drought, drylands, land degradation, land tenure, sustainability Contents 1. Introduction 2. Global Context 3. Land Degradation in Africa Today 3.1. Geographical Regions 3.2. Socio-Economic Aspects 4. Causes and Consequences 4.1. Drought and Other Disasters 4.2. Water Quality and Availability 4.3. Loss of Vegetative Cover 4.4. Loss of Soil Fertility 4.5. Poverty and Population 4.6. Effect of Land Tenure 4.7. Health 5. Combating Desertification 5.1. Past Trends 5.2. Current Attempts to Combat Desertification 5.3. Synergy of the Three Sustainable Development Conventions 5.4. The Role of Science and Technology in Combating Desertification 5.5. Synergy in Environmental Policy Development 6. Future Perspectives: The Way Forward 7. Conclusions Glossary Bibliography Biographical Sketch Summary UNESCO – EOLSS Africa is particularly vulnerable to desertification. Two thirds of the continent consists of desert or drylands.SAMPLE The obvious causes of desertificatiCHAPTERSon and deforestation consist of major ecosystem changes, such as land conversion for various purposes, over- dependence on natural resources and several forms of unsustainable land use. However, the issue of desertification is inseparable from social problems such as poverty and land tenure issues. Politics, war and national disasters affect the movements of people and thus impact on the land. International trade policies as well play a part in land management and/or exploitation. -
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 -
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. -
Road Impact on Deforestation and Jaguar Habitat Loss in The
ROAD IMPACT ON DEFORESTATION AND JAGUAR HABITAT LOSS IN THE MAYAN FOREST by Dalia Amor Conde Ovando University Program in Ecology Duke University Date:_______________________ Approved: ___________________________ Norman L. Christensen, Supervisor ___________________________ Alexander Pfaff ___________________________ Dean L. Urban ___________________________ Randall A. Kramer Dissertation submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy in the University Program in Ecology in the Graduate School of Duke University 2008 ABSTRACT ROAD IMPACT ON DEFORESTATION AND JAGUAR HABITAT LOSS IN THE MAYAN FOREST by Dalia Amor Conde Ovando University Program in Ecology Duke University Date:_______________________ Approved: ___________________________ Norman L. Christensen, Supervisor ___________________________ Alexander Pfaff ___________________________ Dean L. Urban ___________________________ Randall A. Kramer An abstract of a dissertation submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy in the University Program in Ecology in the Graduate School of Duke University 2008 Copyright by Dalia Amor Conde Ovando 2008 Abstract The construction of roads, either as an economic tool or as necessity for the implementation of other infrastructure projects is increasing in the tropical forest worldwide. However, roads are one of the main deforestation drivers in the tropics. In this study we analyzed the impact of road investments on both deforestation and jaguar habitat loss, in the Mayan Forest. As well we used these results to forecast the impact of two road investments planned in the region. Our results show that roads are the single deforestation driver in low developed areas, whether many other drivers play and important role in high developed areas. In the short term, the impact of a road in a low developed area is lower than in a road in a high developed area, which could be the result of the lag effect between road construction and forest colonization. -
Hidden Deforestation in the Brazil - China Beef and Leather Trade 1
Hidden deforestation in the Brazil - China beef and leather trade 1 Hidden deforestation in the Brazil - China beef and leather trade Christina MacFarquhar, Alex Morrice, Andre Vasconcelos August 2019 Key points: China is Brazil’s biggest export market for cattle products, • Cattle ranching is the leading direct driver of deforestation which are a major driver of deforestation and other native and other native vegetation clearance in Brazil, and some vegetation loss in Brazil. This brief identifies 43 companies international beef and leather supply chains are linked to worldwide that are highly exposed to deforestation risk through these impacts. the Brazil-China beef and leather trade, and which have significant potential to help reduce this risk. The brief shows • China (including Hong Kong) is Brazil’s biggest importer of which of these companies have published policies to address beef and leather, and many companies linked to this trade are deforestation risk related to these commodities. It also reveals exposed to deforestation risk. the supplier-buyer relationships between these companies, • We identify 43 companies globally that are particularly exposed and how their connections may mean even those buyers with to the deforestation risk associated with the Brazil-China beef commitments to reduce or end deforestation may not be able to and leather trade and have the potential to reduce these risks. meet them. It then makes recommendations for the next steps companies can take to address deforestation risk. • Most of these companies have not yet published sustainable sourcing policies to address this risk. The companies include cattle processors operating in Brazil, processors and manufacturers operating in China, and • Most appear unable to guarantee that their supply chains are manufacturers and retailers headquartered in Europe and the deforestation-free, because they, or a supplier, lack a strong United States of America (US). -
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. -
Desertification and Agriculture
BRIEFING Desertification and agriculture SUMMARY Desertification is a land degradation process that occurs in drylands. It affects the land's capacity to supply ecosystem services, such as producing food or hosting biodiversity, to mention the most well-known ones. Its drivers are related to both human activity and the climate, and depend on the specific context. More than 1 billion people in some 100 countries face some level of risk related to the effects of desertification. Climate change can further increase the risk of desertification for those regions of the world that may change into drylands for climatic reasons. Desertification is reversible, but that requires proper indicators to send out alerts about the potential risk of desertification while there is still time and scope for remedial action. However, issues related to the availability and comparability of data across various regions of the world pose big challenges when it comes to measuring and monitoring desertification processes. The United Nations Convention to Combat Desertification and the UN sustainable development goals provide a global framework for assessing desertification. The 2018 World Atlas of Desertification introduced the concept of 'convergence of evidence' to identify areas where multiple pressures cause land change processes relevant to land degradation, of which desertification is a striking example. Desertification involves many environmental and socio-economic aspects. It has many causes and triggers many consequences. A major cause is unsustainable agriculture, a major consequence is the threat to food production. To fully comprehend this two-way relationship requires to understand how agriculture affects land quality, what risks land degradation poses for agricultural production and to what extent a change in agricultural practices can reverse the trend. -
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. -
Human Population Growth and Its Implications on the Use and Trends of Land Resources in Migori County, Kenya
HUMAN POPULATION GROWTH AND ITS IMPLICATIONS ON THE USE AND TRENDS OF LAND RESOURCES IN MIGORI COUNTY, KENYA PAULINE TOLO OGOLA A Thesis Submitted in Partial Fulfilment of the Requirements for the Award of the Degree of Master of Environmental Studies (Agroforestry and Rural Development) in the School of Environmental Studies of Kenyatta University NOVEMBR, 2018 1 DEDICATION To my loving parents, Mr. and Mrs. Ogola, With long life He will satisfy you i ACKNOWLEDGEMENT First of all, I am grateful to the Man above who gave me strength and health throughout this study. For sure, His goodness and Mercies are new every day. Secondly, I am greatly indebted to my supervisors Dr. Letema and Dr. Obade for their wise counsel and patience. Thirdly, I would like to convey my utmost gratitude to my parents and siblings for their moral support and prayers. Special thanks to my brother Stephen Ogeda for supporting me financially. Finally, I wish to express many thanks to my colleagues at the Regional Centre for Mapping of Resources for Development and friends who have offered their support in kind and deed. ii TABLE OF CONTENTS DECLARATION………………………………………………………………………… Error! Bookmark not defined. DEDICATION…………………………………………………………………………...i ACKNOWLEDGEMENT……………………………………………………………...ii LIST OF TABLES……………………………………………………………………...vi LIST OF FIGURES……………………………………………………………………vii ABBREVIATIONS AND ACRONYMS……………………………………………….viii ABSTRACT………………………………………………………………………………i x CHAPTER ONE: INTRODUCTION…………………………………………………..1 1.1 Background to the Problem .........................................................................................