Arctic Legal Regime for Environmental Protection
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Analysing Data on Protected Areas Work in Progress
The OECD is developing a method to report a more detailed and harmonised account of countries’ terrestrial and marine protected areas. It applies a harmonised methodology to data from the World Database on Protected Areas. Analysing data on protected areas WORK IN PROGRESS CONTACT Head of Division Nathalie Girouard [email protected] Senior Economist Ivan Haščič [email protected] Statisticians Alexander Mackie [email protected] and Sarah Sentier [email protected] Communications Clara Tomasini [email protected] Image credits: Dormitor Park by Thomas Maluck, Flickr/CC licence. UNSDG. Perereca de folhagem Moisés Silva Lima Flickr/CC Licence. Icon TheNounProject.com http://oe.cd/env-data 2 December 2016 International goals Methodology THE WORLD DATABASE ON PROTECTED AREAS The OECD is developing an improved method to The OECD’s indicators are based on data Union for Conservation of Nature (IUCN) generate more detailed indicators on protected from the World Database on Protected Areas and its World Commission on Protected areas, both terrestrial and marine, for countries (WDPA), which is a geospatial database of Areas (WCPA). across the world. terrestrial and marine protected areas. The WDPA is updated monthly. It contains The WDPA is managed by the United information on more than 200 000 It applies a harmonised methodology to data Nations Environment Programme’s World protected areas. from the World Database on Protected Areas. Conservation Monitoring Centre (UNEP- WCMC) with support from the International CATEGORIES OF MANAGEMENT By 2020, conserve at least 10 per cent of coastal and The World Database on Protected Areas lists z Ia Strict Nature Reserve marine areas, consistent with national and international protected areas designated at national (IUCN z Ib Wilderness Area law and based on best available scientific information. -
Chapter 11 the Natural Ecological Value of Wilderness
204 h The Multiple Values of Wilderness USDA Forest Service. (2002).National and regional project results: 2002 National Chapter 11 Forest Visitor Use Report. Retrieved February 1,2005. from http:Nwww.fs.fed.usl recreation/pmgrams/nvum/ The Natural Ecological Value USDA Forest Service. (200 1). National und regional project results: FY2001 National Foresr ViorUse Report. Retrieved February 1,2005, from http:llwww.fs.fed.usI of Wilderness recreation/pmgrams/nvum/ USDA Forest Service. (2000).National and regional project results: CY20a) Notional Fowst Visitor Use Repor?. Retrieved February 1,2005, from http://www.fs.fed.usl recreation/programs/nvud H. Ken Cordell Senior Research Scientist and Project Leader Vias. A.C. (1999). Jobs folIow people in the nual Rocky Mountain west. Rural Devel- opmenr Perspectives, 14(2), 14-23. USDA Forest Service, Athens, Georgia Danielle Murphy j Research Coordinator, Department of Agricultural and Applied Economics University of Georgia, Athens, Georgia Kurt Riitters Research Scientist USDA Forest Service, Research Triangle Park, North Carolina J. E, Harvard Ill former University of Georgia employee Authors' Note: Deepest appreciation is extended to Peter Landres of the Leopold Wilderness Research Institute for initial ideas for approach, data. and analysis and for a thorough and very helpful review of this chapter. Chapter I I-The Natural Ecological Value of Wilderness & 207 The most important characteristic of an organism is that capacity modem broad-scale external influences, such as nonpoint source pollutants. for self-renewal known QS hcaltk There are two organisms whose - processes of self-renewal have been subjected to human interfer- altered distribution of species, and global climate change (Landres, Morgan ence and control. -
Defining Wilderness Within IUCN
Article for the International Journal of Wilderness, to be published in 2009 Defining wilderness in IUCN Nigel Dudley, Cyril F. Kormos, Harvey Locke and Vance G. Martin The IUCN protected area classification system describes and defines a suite of protected area categories and management approaches suitable for each category, ranging from strictly protected “no-go” reserves to landscape protection and non-industrial sustainable use areas. Wilderness has its own protected area category under IUCN’s classification system, Category Ib, which describes the key objectives of wilderness protection and, more importantly, identifies the limits of what is and is not acceptable in such areas. At the 2008 World Conservation Congress, a new edition of management guidelines for the IUCN categories (Guidelines for Applying Protected Area Management Categories, Dudley 2008) was published following long consultation. Guidance for wilderness protection is now more detailed and precise than in the previous 1994 edition, and as a result will help further the application of this category around the world. We describe the revisions to the new guidelines generally, and some of the implications for wilderness protected areas specifically. Wilderness areas and protected areas The term “wilderness” has several dimensions: a biological dimension, because wilderness refers to mainly ecologically intact areas, and a social dimension, because many people – from urban dwellers to indigenous groups – interact with wild nature, and all humans depend on our planet’s wilderness resource to varying degrees. A wilderness protected area is therefore an area that is mainly biologically intact, is free of modern, industrial infrastructure, and has been set aside so that humans may continue to have a relationship with wild nature. -
Antarctic Treaty Handbook
Annex Proposed Renumbering of Antarctic Protected Areas Existing SPA’s Existing Site Proposed Year Annex V No. New Site Management Plan No. Adopted ‘Taylor Rookery 1 101 1992 Rookery Islands 2 102 1992 Ardery Island and Odbert Island 3 103 1992 Sabrina Island 4 104 Beaufort Island 5 105 Cape Crozier [redesignated as SSSI no.4] - - Cape Hallet 7 106 Dion Islands 8 107 Green Island 9 108 Byers Peninsula [redesignated as SSSI no. 6] - - Cape Shireff [redesignated as SSSI no. 32] - - Fildes Peninsula [redesignated as SSSI no.5] - - Moe Island 13 109 1995 Lynch Island 14 110 Southern Powell Island 15 111 1995 Coppermine Peninsula 16 112 Litchfield Island 17 113 North Coronation Island 18 114 Lagotellerie Island 19 115 New College Valley 20 116 1992 Avian Island (was SSSI no. 30) 21 117 ‘Cryptogram Ridge’ 22 118 Forlidas and Davis Valley Ponds 23 119 Pointe-Geologic Archipelago 24 120 1995 Cape Royds 1 121 Arrival Heights 2 122 Barwick Valley 3 123 Cape Crozier (was SPA no. 6) 4 124 Fildes Peninsula (was SPA no. 12) 5 125 Byers Peninsula (was SPA no. 10) 6 126 Haswell Island 7 127 Western Shore of Admiralty Bay 8 128 Rothera Point 9 129 Caughley Beach 10 116 1995 ‘Tramway Ridge’ 11 130 Canada Glacier 12 131 Potter Peninsula 13 132 Existing SPA’s Existing Site Proposed Year Annex V No. New Site Management Plan No. Adopted Harmony Point 14 133 Cierva Point 15 134 North-east Bailey Peninsula 16 135 Clark Peninsula 17 136 North-west White Island 18 137 Linnaeus Terrace 19 138 Biscoe Point 20 139 Parts of Deception Island 21 140 ‘Yukidori Valley’ 22 141 Svarthmaren 23 142 Summit of Mount Melbourne 24 118 ‘Marine Plain’ 25 143 Chile Bay 26 144 Port Foster 27 145 South Bay 28 146 Ablation Point 29 147 Avian Island [redesignated as SPA no. -
Antarctica's Wilderness Has Declined to the Exclusion of Biodiversity
bioRxiv preprint doi: https://doi.org/10.1101/527010; this version posted January 22, 2019. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC-ND 4.0 International license. Antarctica’s wilderness has declined to the exclusion of biodiversity Rachel I. Leihy1, Bernard W.T. Coetzee2, Fraser Morgan3, Ben Raymond4, Justine D. Shaw5, Aleks Terauds4, and Steven L. Chown1 1School of Biological Sciences, Monash University, Victoria 3800, Australia. 2Global Change Institute, University of the Witwatersrand, WITS 2050, Johannesburg, South Africa. 3Landcare Research New Zealand, Private Bag 92170, Auckland Mail Centre, Auckland 1142, New Zealand. 4Australian Antarctic Division, Department of the Environment and Energy, 203 Channel Highway, Kingston, Tasmania 7050, Australia. 5School of Biological Sciences, The University of Queensland, Queensland 4072, Australia. Recent assessments of the biodiversity value of Earth’s dwindling wilderness areas1,2 have emphasized the whole of Antarctica as a crucial wilderness in need of urgent protection3. Whole-of-continent designations for Antarctic conservation remain controversial, however, because of widespread human impacts and frequently used provisions in Antarctic law for the designation of specially protected areas to conserve wilderness values, species and ecosystems4,5. Here we investigate the extent to which Antarctica’s wilderness encompasses its biodiversity. We assembled a comprehensive record of human activity on the continent (~ 2.7 million localities) and used it to identify unvisited areas ≥ 10 000 km2 (1,6-8) (i.e. Antarctica’s wilderness areas) and their representation of biodiversity. -
Kaibab National Forest
United States Department of Agriculture Kaibab National Forest Forest Service Southwestern Potential Wilderness Area Region September 2013 Evaluation Report The U.S. Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, age, disability, and where applicable, sex, marital status, familial status, parental status, religion, sexual orientation, genetic information, political beliefs, reprisal, or because all or part of an individual’s income is derived from any public assistance program. (Not all prohibited bases apply to all programs.) Persons with disabilities who require alternative means of communication of program information (Braille, large print, audiotape, etc.) should contact USDA’s TARGET Center at (202) 720-2600 (voice and TTY). To file a complaint of discrimination, write to USDA, Director, Office of Civil Rights, 1400 Independence Avenue, SW, Washington, DC 20250-9410, or call (800) 795-3272 (voice) or (202) 720-6382 (TTY). USDA is an equal opportunity provider and employer. Cover photo: Kanab Creek Wilderness Kaibab National Forest Potential Wilderness Area Evaluation Report Table of Contents Introduction ................................................................................................................................................. 1 Inventory of Potential Wilderness Areas .................................................................................................. 2 Evaluation of Potential Wilderness Areas ............................................................................................... -
Wilderness Fire Management in a Changing World
STEWARDSHIP Wilderness Fire Management in a Changing World BY CAROL MILLER everal strategies are available for reducing accumu- results from either human or natural causes, and the man- lated forest fuels and their associated risks, including agement objective is to stop the spread of the fire and S naturally or accidentally ignited wildland fires, man- extinguish it at the least cost (USDA and USDI 2001). In agement ignited prescribed fires, and a variety of mechanical some cases, concerns about firefighter safety and suppres- and chemical methods (Omi 1996). However, a combina- sion costs will result in a less aggressive suppression tion of policy, law, philosophy, and logistics suggest there is response to a wildfire, with features of the landscape being a more limited set of fuels man- used to allow fire to burn within a designated area. WFU is agement activities that are the management of naturally ignited wildland fires to pro- appropriate in wilderness (Bryan tect, maintain, and enhance resources in predefined areas 1997; Parsons and Landres 1998; outlined in fire management plans (USDA and USDI 2001). Nickas 1998). Naturally ignited The management objective is to allow fire, as nearly as pos- wildland fires is the commonly sible, to function in its natural ecological role. In some cases, preferred fuels management strat- certain suppression tactics might be used with WFU to pro- egy in wilderness (Miller 2003), tect life, property, or specific values of concern. Recently, with management-ignited pre- there has been discussion about effectively dissolving the scribed fire being considered in distinction between wildfire and WFU, and managing all some cases (Landres et al. -
Antarctic Geoconservation: a Review of Current Systems and Practices
Environmental Conservation (2016) 43 (2): 97–108 C Foundation for Environmental Conservation 2016. This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution, and reproduction in any medium, provided the original work is properly cited. doi:10.1017/S0376892915000387 Antarctic geoconservation: a review of current systems and practices KEVIN A. HUGHES1 ∗, JERÓNIMO LÓPEZ-MARTÍNEZ2 ,JANEE.FRANCIS1 , J. ALISTAIR CRAME1 , LUIS CARCAVILLA3 , KAZUYUKI SHIRAISHI4,5, TOMOKAZU HOKADA4,5 AND AKIRA YAMAGUCHI4,5 1British Antarctic Survey, Natural Environment Research Council, High Cross, Madingley Road, Cambridge CB3 0ET, UK, 2Universidad Autónoma de Madrid, Facultad de Ciencias, Departamento de Geología y Geoquímica, 28049 Madrid, Spain, 3Geological Survey of Spain, Rios Rosas, 23, 28003 Madrid, Spain, 4National Institute of Polar Research (NIPR), 10–3 Midori-cho, Tachikawa-shi, Tokyo 190–8518, Japan, and 5SOKENDAI (The Graduate University for Advanced Studies), 10–3 Midori-cho, Tachikawa-shi, Tokyo 190–8518, Japan Date submitted: 15 May 2015; Date accepted: 29 October 2015; First published online 9 February 2016 SUMMARY the continent, and the pursuit of geological knowledge has had a strong influence on its historical values (Fig. 1 and 2). For The prohibition of commercial mineral resource example, Captain Scott’s doomed South Pole party of 1912 extraction through the Antarctic Treaty System has collected 16 kg of rocks including fossil leaves of Glossopteris removed one significant source of potential damage to indica, which provided evidence that Antarctica was once part Antarctica’s geological and geomorphological values. of the larger supercontinent of Gondwana. -
ASOC Report on ATCM XXIX
ASOC Report on XXIX ATCM – Edinburgh 2006 The Antarctic and Southern Ocean Coalition ASOC Secretariat 1630 Connecticut Ave NW Washington, DC 20009 USA Tel +1 202 234-2480 Fax +1 202 387-4823 Email : [email protected] www.asoc.org August 10, 2006 ASOC REPORT ON THE XXIX ANTARCTIC TREATY CONSULTATIVE MEETING Edinburgh, United Kingdom 12-23 June 2006 1 ASOC Report on XXIX ATCM – Edinburgh 2006 EXECUTIVE SUMMARY BACKGROUND 1. Antarctic Treaty Consultative Meetings (ATCMs) give effect to obligations under the 1959 Antarctic Treaty, and the 1991 Protocol on Environmental Protection to the Antarctic Treaty. 2. ATCMs are hosted by Consultative Parties (essentially voting members – currently 28) in English-language alphabetical order. All Consultative Parties attended the Edinburgh meeting. There are also 17 Non-Consultative Parties – non-voting members, although the majority do not regularly attend ATCMs (7 attended in Edinburgh). The ATCM lasts two weeks, and conducts its business through a number of Working Groups – presently four: Legal and Institutional Affairs, Tourism and Non-Governmental Activities, Operational Matters and the Committee for Environmental Protection (CEP). 3. The Antarctic and Southern Ocean Coalition (ASOC) has participating ‘Expert’ status at ATCMs. It is the only environmental non-governmental group with such access. IUCN and UNEP are also invited ‘Experts’. 4. The XXIX ATCM was held in Edinburgh from 12 – 23 June 2006. In addition, a pre-CEP Workshop on “Antarctica’s Future Environmental Challenges” was held on June 9-10. -
Wilderness Air Quality Value Plan for the Shoshone National Forest
Wilderness Air Quality Value Plan Shoshone National Forest Clocktower Creek and Wapiti Ridge, Washakie Wilderness Prepared by: /s/ Greg Bevenger __________________________________ Greg Bevenger, Air Program Manager Recommended by: /s/ Bryan Armel ______________________________________________ Bryan Armel, Resources Staff Officer Recommended by: /s/ Loren Poppert ______________________________________________ Loren Poppert, Recreation Staff Officer Approved by: /s/ Rebecca Aus ______________________________________________ Rebecca Aus, Forest Supervisor May 2010 Wilderness Air Quality Value Plan Introduction Background As part of the USDA Forest Service effort to better understand and monitor wilderness areas, the agency has adopted the 10-Year Wilderness Stewardship Challenge (Forest Service 2005). The 10-Year Wilderness Stewardship Challenge was developed by the Chief’s Wilderness Advisory Group (WAG) as a quantifiable measurement of the Forest Service’s success in wilderness stewardship. The goal identified by the Wilderness Advisory Group, and endorsed by the Chief, is to bring each wilderness under Forest Service management to a minimum stewardship level by the year 2014, the fiftieth anniversary of the Wilderness Act. The Challenge was initiated in fiscal year 2005. The Challenge contains ten items that highlight elements of wilderness stewardship. These elements are 1) the natural role of fire, 2) invasive plants, 3) air quality, 4) education, 5) protection of recreational opportunities, 6) recreational site inventory, 7) outfitters -
Antarctic Specially Protected Areas As Tools for Conservation: an Assessment of Purpose, Placement and Effect
PCAS 17 (2014/2015) Critical Literature Review (ANTA602) Antarctic Specially Protected Areas as tools for conservation: An assessment of purpose, placement and effect Bridget McNeill Student ID: 91008903 Word count: 2945 Abstract Offering the highest level of protection under the current Antarctic Treaty System, Antarctic Specially Protected Areas are often considered a key tool in the conservation of terrestrial Antarctica (Shaw et al 2014). However as conservation science evolves, and approaches to conservation planning become more systematic, the capability of these areas to meet long-term Antarctic conservation objectives has been questioned. To address this, both the placement and management of existing Antarctic Specially Protected Areas is reviewed, in order to assess whether, as a system, Antarctic Specially Protected Areas 1) designate adequate area, representative Antarctic biodiversity, and 2) effectively separate it from threatening processes. Finding that in the short term, stricter compliance with management guidelines and monitoring is required by Treaty Parties, and in the long term, that meeting representativeness and comprehensiveness requirements is impeded by both a gap in available data and the placement of existing system, it is clear that both the management and designation processes of ASPA’s requires review if Antarctic conservation objectives are to be achieved. Contents Introduction ...................................................................................................................................................... -
Protected Areas Guidelines
ATCM Document GUIDELINES FOR IMPLEMENTATION OF THE FRAMEWORK FOR ANTARCTIC PROTECTED AREAS Published by the Council of Managers of National Antarctic Programs (COMNAP) on behalf of the Antarctic Treaty Consultative Meetings (ATCM) Copyright © ATCM 2000 COMNAP Secretariat GPO Box 824 Hobart Tasmania 7001 AUSTRALIA Tel: +61 (0)3 6233 5498 Fax: +61 (0)3 6233 5497 GUIDELINES FOR IMPLEMENTATION OF THE FRAMEWORK FOR PROTECTED AREAS SET FORTH IN ARTICLE 3, ANNEX V OF THE ENVIRONMENTAL PROTOCOL CONTENTS PART I: INTRODUCTION 2 1.1 The Antarctic Treaty System and Protected Areas 2 1.2 Aim of the Guidelines 2 1.3 Structure of the Guidelines 3 PART II: ASSESSING AREAS FOR PROTECTION 4 2.1 Assessing Values to be Protected (Article 3(1)) 4 2.2 Assessment of Potential Protection and Use Category (Article 3(2a-i)) 5 2.3 Quality Criteria 6 2.4 Environmental Risk Assessment 8 PART III: DEFINING AREAS FOR PROTECTION 10 3.1 Tools for Assisting in Selecting Protected Areas 10 3.2 Area Design 10 3.3 Feasibility Criteria 10 PART IV: PROPOSING AREAS FOR PROTECTION 13 4.1 Drafting Management Plans for Proposed ASPAs 13 4.2 Further Steps in the Designation Process 13 APPENDIX: Articles 3(1) and 3(2) of Annex V 14 REFERENCES AND BIBLIOGRAPHY 15 PART I: INTRODUCTION 1.1 The Antarctic Treaty System and Protected Areas A variety of instruments have been developed within the Antarctic Treaty system to help protect special places such as important wildlife breeding areas, fragile plant communities, cold desert ecosystems and historic places. These instruments have included the Agreed Measures for the Conservation of Antarctic Fauna and Flora and numerous recommendations to Parties.