The Role of Landscape Connectivity in Planning and Implementing Conservation and Restoration Priorities Deborah A
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Landscape Connectivity Science and Practice: Ways Forward for Large Ranging Species and Their Landscapes
LANDSCAPE CONNECTIVITY SCIENCE AND PRACTICE: WAYS FORWARD FOR LARGE RANGING SPECIES AND THEIR LANDSCAPES 1 Acknowledgements: This report was developed following the Landscape Connectivity Workshop held at and hosted by WWF India, Delhi in May 2018. We are grateful to the following people who provided valuable input, facilitation and compilation of notes throughout and following the workshop: Hamsini Bijlani, Dipankar Ghose (WWF India), Nilanga Jayasinghe (WWF US), Nitin Seker (WWF India), Indira Akoijam (WWF India), Thu Ba Huynh (WWF Tigers Alive). Suggested citation: WWF Tigers Alive (2020). Landscape Connectivity Science and Practice: Ways forward for large ranging species and their landscapes. Workshop Report, WWF Tigers Alive, WWF International. Workshop report editors: Ashley Brooks (WWF Tigers Alive), Hamsini Bijlani. Case study report researcher and author: Kyle Lukas Report prepared by: WWF Tigers Alive Published in: 2020 by WWF – World Wide Fund for Nature (Formerly World Wildlife Fund), Gland, Switzerland. Any reproduction in full or in part must mention the title and credit the above- mentioned publisher as the copyright owner. For more information please contact: Ashley Brooks. [email protected] WWF Tigers Alive is an initiative of WWF that supports tiger range countries achieve their commitments under the Global Tiger Recovery Program to double the number of tigers by 2022. WWF is one of the world’s largest and most experienced independent conservation organizations, with over 5 million supporters and a global network active in more than 100 countries. WWF’s mission is to stop the degradation of the planet’s natural environment and to build a future in which humans live in harmony with nature, by: conserving the world’s biological diversity, ensuring that the use of renewable natural resources is sustainable, and promoting the reduction of pollution and wasteful consumption. -
Sustainable Forest Management Policy
SUSTAINABLE FOREST MANAGEMENT POLICY DIVISION OF FORESTRY MINISTRY OF NATURAL RESOURCES, ENVIRONMENT & TOURISM S E P T E M B E R 2 0 1 8 TABLE OF CONTENTS 01 - Introduction 02 - Definition of Forest and Sustainable Forest Management 02 - Development of Palau's Sustainable Forest Management Policy 03 - Use of Palau's Sustainable Forest Management Policy (SFM) 04 - Linkages with Other Relevant Policies, Strategies, and Plans 07 - Broad Policy Description 07 - Vision 08 - Policy Goal 08 - Guiding Principles 09 - Sustainable Forest Management Policy Objectives, Outcomes, Directives and Indicators 10 - Focal Area 1 12 - Focal Area 2 14 - Focal Area 3 18 - Implementation Arrangement for Sustainable Forest Management 18 - Monitoring and Evaluation (M&E) Strategy 19 - Sustainable Forest Management Policy Review 19 - The Nature and Extent of Palau's Forest Resources 20 - Palau Forest Types 26 - Pressure on Palau's Forest 27 - Palau Forest Situation Analysis Conceptual Model 28 - Acronyms 29 - References INTRODUCTION The Republic of Palau values the contribution of forest ecosystems to the social, economic and environmental wellbeing of its citizens. Forests contribute to the national wellbeing by controlling soil erosion, improving soil fertility and regulating water flow. It contributes to the national economy through the production of wood for artisan crafts and construction. Forest contribution to the economy also includes its recreational value to terrestrial tourism enterprises. Finally, forests enable the Palauan culture to flourish its value as a repository of culturally significant plant resources. The continued use of these forest resources as medicines, traditional building materials and crafts facilitates the maintenance and dissemination of Palauan traditional ecological knowledge. -
Review of Areas of Outstanding Natural Beauty and National Parks 2015
National Landscapes: Realising their Potential The Review of Designated Landscapes in Wales Final Report Professor Terry Marsden John Lloyd-Jones Dr Ruth Williams 31 July 2015 Map 1: The Statutory Designated Landscapes of Wales 2 Contents Chair’s Foreword………………………………………………………………………. 4 Executive Summary and Recommendations………………………………………. 7 Chapter 1. Introduction………………………………………………………….. 27 Chapter 2. How We Evidenced Stage Two…………………………………… 31 Chapter 3. Responses to the Call for Evidence………………………………. 35 Chapter 4. A Changing Context for the Designated Landscapes in Wales... 37 Chapter 5. The Existing Model of Designated Landscape Governance in… 55 Wales Chapter 6. The Principles and Purposes of Wales’ Designated……………. 103 Landscapes Chapter 7. A Vision for the National Landscapes of Wales…………………. 113 Chapter 8. A New Framework for the Governance of Wales’ National…….. 129 Landscapes Appendix Appendix i. The Review of Designated Landscapes in Wales………………. 166 Stage One Recommendations Appendix ii. Stage Two Call for Evidence Contributions……………………… 170 Appendix iii. Stage Two Evidence Gathering Sessions……………………….. 172 Appendix iv. Case Studies………………………………………………………… 176 Appendix v. Bibliography…………………………………………………………. 227 Appendix vi. National Park Management Plan…………………………………. 235 and State Of the Park Report Indicators Appendix vii. Finance Flow Diagram……………………………………………… 242 Appendix viii Governance of Contracts Flow Diagram…………………………. 243 Appendix ix. Planning Development Management Flow Diagram……………. 244 Appendix x. Planning Enforcement Flow Diagram…………………………….. 245 3 Chair’s Foreword Over the past year I along with panel members Dr Ruth Williams and John Lloyd Jones have been working for the Minister for Natural Resources to undertake an independent review of the Designated Landscapes of Wales. The Minister wants to “‘ensure that our designated landscapes are best equipped to meet current and future challenges while building upon their internationally recognised status”. -
Forest Management Guide for Boreal Landscapes
Forest Management Guide for Boreal Landscapes 2014 Cette publication spécialisée n’est disponible qu’en anglais en vertu du Règlement 411/10, qui en exempte l’application de la Loi sur les services en français. Forest Management Guide for Boreal Landscapes 2014, Queen’s Printer for Ontario Printed in Ontario, Canada Publications and price lists are available from this office: ServiceOntario Publications 300 Water Street P.O. Box 7000 Peterborough, ON K9J 8M5 1-800-668-9938 www.serviceontario.ca/publications Telephone inquiries should be directed to the Service Ontario Contact Centre: General Inquiry 1-800-668-9938 Renseignements en Français 1-800-667-1840 FAX (705) 755-1677 Other government publications are available from: ServiceOntario Publications, Market level (lower), 777 Bay St., Toronto Visit the Ontario’s Forests website at: http://www.ontario.ca/forests Visit the Ontario Ministry of Natural Resources website at: http://www.ontario.ca/mnr Cover photos provided by: Ted Armstrong, Phil Elkie, Lindsay MacLean and Kevin Ride. How to cite this manual: OMNR. March 2014. Forest Management Guide for Boreal Landscapes. Toronto: Queen’s Printer for Ontario. 104 pp. MNR Number: 62826 (Print) MNR Number: 62827 (PDF) ISBN: 978-1-4606-3670-1 (Print) ISBN: 978-1-4606-3671-8 (PDF) Forest Management Guide for Boreal Landscapes Table of Contents List of Figures..................................................................................................................................v List of Tables..................................................................................................................................vii -
Improving Habitat and Connectivity Model Predictions with Multi-Scale Resource Selection Functions from Two Geographic Areas
Landscape Ecol (2019) 34:503–519 https://doi.org/10.1007/s10980-019-00788-w (0123456789().,-volV)(0123456789().,-volV) RESEARCH ARTICLE Improving habitat and connectivity model predictions with multi-scale resource selection functions from two geographic areas Ho Yi Wan . Samuel A. Cushman . Joseph L. Ganey Received: 22 May 2018 / Accepted: 18 February 2019 / Published online: 4 March 2019 Ó This is a U.S. government work and its text is not subject to copyright protection in the United States; however, its text may be subject to foreign copyright protection 2019 Abstract converted the models into landscape resistance sur- Context Habitat loss and fragmentation are the most faces and used simulations to model connectivity pressing threats to biodiversity, yet assessing their corridors for the species, and created composite impacts across broad landscapes is challenging. habitat and connectivity models by averaging the Information on habitat suitability is sometimes avail- local and non-local models. able in the form of a resource selection function model Results While the local and the non-local models developed from a different geographical area, but its both performed well, the local model performed best applicability is unknown until tested. in the part of the study area where it was built, but Objectives We used the Mexican spotted owl as a performed worse in areas that are beyond the extent of case study to demonstrate how models developed from the data used to train it. The composite habitat model different geographic areas affect our predictions for improved performances over both models in most habitat suitability, landscape resistance, and connec- cases. -
Guidelines for Wildlife and Traffic in the Carpathians
Wildlife and Traffic in the Carpathians Guidelines how to minimize the impact of transport infrastructure development on nature in the Carpathian countries Wildlife and Traffic in the Carpathians Guidelines how to minimize the impact of transport infrastructure development on nature in the Carpathian countries Part of Output 3.2 Planning Toolkit TRANSGREEN Project “Integrated Transport and Green Infrastructure Planning in the Danube-Carpathian Region for the Benefit of People and Nature” Danube Transnational Programme, DTP1-187-3.1 April 2019 Project co-funded by the European Regional Development Fund (ERDF) www.interreg-danube.eu/transgreen Authors Václav Hlaváč (Nature Conservation Agency of the Czech Republic, Member of the Carpathian Convention Work- ing Group for Sustainable Transport, co-author of “COST 341 Habitat Fragmentation due to Trans- portation Infrastructure, Wildlife and Traffic, A European Handbook for Identifying Conflicts and Designing Solutions” and “On the permeability of roads for wildlife: a handbook, 2002”) Petr Anděl (Consultant, EVERNIA s.r.o. Liberec, Czech Republic, co-author of “On the permeability of roads for wildlife: a handbook, 2002”) Jitka Matoušová (Nature Conservation Agency of the Czech Republic) Ivo Dostál (Transport Research Centre, Czech Republic) Martin Strnad (Nature Conservation Agency of the Czech Republic, specialist in ecological connectivity) Contributors Andriy-Taras Bashta (Biologist, Institute of Ecology of the Carpathians, National Academy of Science in Ukraine) Katarína Gáliková (National -
On the Authenticity of De-Extinct Organisms, and the Genesis Argument Douglas Campbell University of Canterbury, New Zealand
Animal Studies Journal Volume 6 | Number 1 Article 5 2017 On the Authenticity of De-extinct Organisms, and the Genesis Argument Douglas Campbell University of Canterbury, New Zealand Follow this and additional works at: https://ro.uow.edu.au/asj Part of the Art and Design Commons, Australian Studies Commons, Creative Writing Commons, Digital Humanities Commons, Education Commons, Feminist, Gender, and Sexuality Studies Commons, Film and Media Studies Commons, Fine Arts Commons, Philosophy Commons, Social and Behavioral Sciences Commons, and the Theatre and Performance Studies Commons Recommended Citation Campbell, Douglas, On the Authenticity of De-extinct Organisms, and the Genesis Argument, Animal Studies Journal, 6(1), 2017, 61-79. Available at:https://ro.uow.edu.au/asj/vol6/iss1/5 Research Online is the open access institutional repository for the University of Wollongong. For further information contact the UOW Library: [email protected] On the Authenticity of De-extinct Organisms, and the Genesis Argument Abstract Are the methods of synthetic biology capable of recreating authentic living members of an extinct species? An analogy with the restoration of destroyed natural landscapes suggests not. The er stored version of a natural landscape will typically lack much of the aesthetic value of the original landscape because of the different historical processes that created it – processes that involved human intentions and actions, rather than natural forces acting over millennia. By the same token, it would appear that synthetically recreated versions of extinct natural organisms will also be less aesthetically valuable than the originals; that they will be, in some strong sense, ‘inauthentic’, because of their peculiar history and mode of origin. -
Ecology-Based Landscape Planning and Management
Synthesis Ecology-Based Landscape Planning and Management Thomas R. Crow 1 The Three Faces of Sustainability The words "sustain" or "sustainable" are commonly found in the mission statements of resource management agencies. The mission of the USDA Forest Service, for example, is to "sustain the health, diversity, and productivity of the Nation's forests and grasslands to meet the needs of present and future generations." Sustaining the health, diversity, and productivity of a resource has certain fundamental require- ments (Thayer 1989; Fedkiw et al. 2004). They start with a commitment to manage land and the water resources for the long term. It requires connecting the people living in the landscape with the natural resources that support their lives. It has to be inclusive of all sectors and functions of society by embracing meaningful civic involvement. And finally, sustaining the health, diversity and productivity of natural resources must create opportunities and preserve choices for people. These require- ments necessitate a comprehensive approach in which economic, environmental, and social sustainability are given equal weight and are considered concurrently. Landscape ecology provides a conceptual as well as an operational framework for considering the three faces of sustainability. 2 Moving from Concept to Practice The five chapters in this section support moving from concept to practice. Practic- ing sustainability within the context of landscapes is the unifying theme among the chapters. Each chapter illustrates the utility of a landscape perspective for considering sustainabilityin a variety of social and environmental settings. In Chapter 14, Azevedo et al. evaluated the changes in landscape structure and function that occur due to the application of a forest certification program, the Sustainable Forestry Initiative (SFI), in Texas, USA. -
FSC's Contribution to Forest Restoration
Forest Stewardship Council® FSC® International December 2017 FSC’S CONTRIBUTION TO FOREST RESTORATION Forest Restoration – FSC is on board! Although the Forest Stewardship Council (FSC) is well known for promoting sustainable forest management, it is less known for forest (and landscape) restoration. FSC certification means that in spite of forest management interventions forests remain for generations to come, and that their ecological functioning is maintained. Therefore FSC’s biggest contribution is in preventing the need for forest restoration. FSC certification is also being used in forest restoration projects. In addition, restoration has become an explicit objective in the revised FSC Principles & Criteria for Forest Stewardship (Version 5, 2012), in a number of ways. FSC certification plays a role in achieving the ambitious targets set by the Bonn Challenge on forest restoration, particularly to move from commitments to reality. It has therefore joined the Global Partnership on Forest and Landscape Restoration and is keen to work with the other organizations in this partnership for concrete results. FSC also offers a practical tool that contributes to successful restoration of former forest lands that are not yet certified. Successful stakeholder engagement procedures and practices developed by FSC can help make forest restoration a success by effectively engaging local communities. Moreover, the commitment of reforestation projects to FSC certification can trigger investments and provide a better economic perspective. The FSC perception of forest restoration FSC’s perception of forest restoration is pragmatic. We are not necessarily aiming for restoration into the original, virgin ecosystems as they existed before human intervention. Ongoing pressures due to population growth, in particular where forests are most under threat, and even faster growth of demand for resources, create increasing competition for land and natural resource uses. -
Green Infrastructure Design for Transport Projects: a Road Map To
GREEN INFRASTRUCTURE DESIGN FOR TRANSPORT PROJECTS A ROAD MAP TO PROTECTING ASIA’S WILDLIFE BIODIVERSITY DECEMBER 2019 ASIAN DEVELOPMENT BANK GREEN INFRASTRUCTURE DESIGN FOR TRANSPORT PROJECTS A ROAD MAP TO PROTECTING ASIA’S WILDLIFE BIODIVERSITY DECEMBER 2019 ASIAN DEVELOPMENT BANK Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) © 2019 Asian Development Bank 6 ADB Avenue, Mandaluyong City, 1550 Metro Manila, Philippines Tel +63 2 8632 4444; Fax +63 2 8636 2444 www.adb.org Some rights reserved. Published in 2019. ISBN 978-92-9261-991-6 (print), 978-92-9261-992-3 (electronic) Publication Stock No. TCS189222 DOI: http://dx.doi.org/10.22617/TCS189222 The views expressed in this publication are those of the authors and do not necessarily reflect the views and policies of the Asian Development Bank (ADB) or its Board of Governors or the governments they represent. ADB does not guarantee the accuracy of the data included in this publication and accepts no responsibility for any consequence of their use. The mention of specific companies or products of manufacturers does not imply that they are endorsed or recommended by ADB in preference to others of a similar nature that are not mentioned. By making any designation of or reference to a particular territory or geographic area, or by using the term “country” in this document, ADB does not intend to make any judgments as to the legal or other status of any territory or area. This work is available under the Creative Commons Attribution 3.0 IGO license (CC BY 3.0 IGO) https://creativecommons.org/licenses/by/3.0/igo/. -
How Should We Measure Landscape Connectivity?
Landscape Ecology 15: 633–641, 2000. 633 © 2000 Kluwer Academic Publishers. Printed in the Netherlands. How should we measure landscape connectivity? Lutz Tischendorf∗ & Lenore Fahrig Ottawa-Carleton Institute of Biology, Carleton University, 1125 Colonel By Drive, Ottawa, Canada K1S 5B6 (∗Current address: Busestrasse 76, 28213 Bremen, Germany; E-mail: [email protected]) Received 9 April 1999; Revised 27 December 1999; Accepted 7 February 2000 Abstract The methods for measuring landscape connectivity have never been compared or tested for their responses to habitat fragmentation. We simulated movement, mortality and boundary reactions across a wide range of land- scape structures to analyze the response of landscape connectivity measures to habitat fragmentation. Landscape connectivity was measured as either dispersal success or search time, based on immigration into all habitat patches in the landscape. Both measures indicated higher connectivity in more fragmented landscapes, a potential for problematic conclusions for conservation plans. We introduce cell immigration as a new measure for landscape connectivity. Cell immigration is the rate of immigration into equal-sized habitat cells in the landscape. It includes both within- and between-patch movement, and shows a negative response to habitat fragmentation. This complies with intuition and existing theoretical work. This method for measuring connectivity is highly robust to reductions in sample size (i.e., number of habitat cells included in the estimate), and we hypothesize that it therefore should be amenable to use in empirical studies. The connectivity measures were weakly correlated to each other and are therefore generally not comparable. We also tested immigration into a single patch as an index of connectivity by comparing it to cell immigration over the landscape. -
Wildlife Corridors 15 15
NORTH EAST NEW SOUTH WALES Wildlife Corridors 15 15 What are wildlife corridors? pollination of plants and other natural functions required for ecosystem health. A wildlife corridor is a link of wildlife The likely result is severe biodiversity habitat, generally native vegetation, which decline and local extinction of sensitive joins two or more larger areas of similar species. wildlife habitat. Corridors are critical for NOTE the maintenance of ecological processes Corridors play an extremely important role NOTE including allowing for the movement of in the maintenance of biodiversity, but they animals and the continuation of viable can only partly compensate for the overall populations. habitat loss produced by the fragmentation of the natural landscape. It is important, By providing landscape connections therefore, that vegetation remnants and between larger areas of habitat, corridors vegetated corridors are maintained and enable migration, colonisation and enhanced as a network across all lands interbreeding of plants and animals. both private and public. In this way private Corridors can consist of a sequence of landscapes can contribute to wider stepping stones across the landscape landscape conservation efforts by (discontinuous areas of habitat such as enhancing and linking existing reserves paddock trees, wetlands and roadside and conservation networks. vegetation), continuous lineal strips of vegetation and habitat (such as riparian NPWS Geoff Biddle/ strips, ridge lines etc.), or they maybe parts of a larger habitat area selected for its known or likely importance to local fauna. Why are corridors important? Habitat loss and fragmentation are the two main contributors to continuing biodiversity Aerial photograph showing the importance decline across the landscape.