Development of an Effective Forest Fire Management Strategy for Bhutan
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Chapter 3 Quantifying Illegal Logging and Related Timber Trade
3 QUANTIFYING ILLEGAL LOGGING AND RELATED TIMBER TRADE 3 QUANTIFYING ILLEGAL LOGGING AND RELATED TIMBER TRADE Chapter 3 Quantifying Illegal Logging and Related Timber Trade Lead author: Jianbang Gan Contributing authors: Paolo Omar Cerutti, Mauro Masiero, Davide Pettenella, Nicola Andrighetto and Tim Dawson CONTENTS 3.1 Introduction 38 3.2 Species, Markets and Trade Patterns of Wood Products 38 3.2.1 Species Rarity, Value and Illegality 38 3.2.2 Domestic, Regional and Global Wood Products Markets and Supply Chains 38 3.2.3 Global Trade Patterns of Wood Products 40 3.2.4 Major Producers and Importers of Tropical Timber 41 3.2.5 Financial Flows Associated with Illegal Logging and Related Timber Trade 42 3.3 Existing Estimates on Illegal Logging and Related Timber Trade 43 3.3.1 Estimation Methods 43 3.3.2 Existing Estimates and their Comparisons 43 3.4 Following the Trade Data 46 3.4.1 Recent Trends in International Trade Flows of Illegal Wood Products 46 3.4.2 New Developments in Illegal Logging and Related Timber Trade 51 3.5 Conclusions 52 References 54 Appendices 56 Appendix 3.1 Methods for Estimating Illegal Logging and Related Timber Trade 56 Appendix 3.2 Country Codes Used in Figure 3.4 58 37 3 QUANTIFYING ILLEGAL LOGGING AND RELATED TIMBER TRADE 3.1. Introduction This phenomenon coupled with illegal activities can create a vicious cycle among value, rarity (scarcity) and Understanding the magnitude of illegal logging and re- illegality (see Figure 3.1). Many rare and endangered tree lated timber trade as well as illegal trade flows is criti- species have higher economic values than others because cal to addressing the problem. -
National Forest Policy
NATIONAL FOREST POLICY 1988 GOVERNMENT OF INDIA MINISTRY OF ENVIRONMENT AND FORESTS NEW DELHI No. 3-1/86-FP Ministry of Environment and Forests (Department of Environment, Forests & Wildlife) Paryavaran Bhavan, CGO Complex, Lodi Road, New Delhi - 110003. Dated the 7th December, 1988. RESOLUTION National Forest Policy, 1988 1. PREAMBLE 1.1. In Resolution No.13/52/F, dated the 12th May, 1952, the Government of India in the erstwhile Ministry of Food and Agriculture enunciated a Forest Policy to be followed in the management of State Forests in the country. However, over the years,* forests in the country have suffered serious depletion. This is attributable to relentless pressures arising from ever-increasing demand for fuel- wood, fodder and timber; inadequacy of protection measures; diversion of forest lands to non-forest uses without ensuring compensatory afforestation and essential environmental safeguards; and the tendency to look upon forests as revenue earning resource. The need to review the situation and to evolve, for the future, a new strategy of forest conservation has become imperative. Conservation includes preservation, maintenance, sustainable utilisation, restoration, and enhancement of the natural environment. It has thus become necessary to review and revise the National Forest Policy. 2. BASIC OBJECTIVES 2.1 The basic objectives that should govern the National Forest Policy - are the following: • Maintenance of environmental stability through preservation and, where necessary, restoration of the ecological balance that has been adversely disturbed by serious depletion of the forests of the country. • Conserving the natural heritage of the country by preserving the remaining natural forests with the vast variety of flora and fauna, which represent the remarkable biological diversity and genetic resources of the country. -
Forest Department Ministry of Environment and Forests
Government of the People’s Republic of Bangladesh Forest Investment Programme 2017 Forest Department Ministry of Environment and Forests Table of Contents Abbreviations Executive Summary Chapter 1: Description of the Country and Sector Context 1.1 Background 1.2 Land Use Pattern in Bangladesh 1.3 Definition of Forests in Bangladesh 1.4 Forest Types 1.5 Trends in Area under Forests, Deforestation and Forest Degradation 1.6 Role of Agroforestry, Homestead Gardens and Private Plantations 1.7 Role of Coastal Mangroves 1.8 Afforestation, Reforestation and Coastal Mangrove Afforestation 1.9 CO2 emissions from LULUCF (Land Use, Land-Use Change and Forest) Sector 1.10 Carbon Stocks in Forests and Trends 1.11 Drivers of Deforestation 1.12 Challenges for the Forest sector in Bangladesh 1.13 Objectives of Forest Investment Programme Chapter 2: Identification of Opportunities for Greenhouse Gas Abatement 2.1 Introduction 2.2 Seventh (7th) Five Year Plan: Goals and Programmes 2.3 National Forest Policy 2016 (Proposed) 2.4 Forestry Master Plan (FMP)– 2016: Strategies and Targets 2.5 Country Investment Plan (CIP-2016–2021) 2.6 National Conservation Strategy (NCS) 2.7 INDC (Intended Nationally Determined Contributions) 2.8 Bangladesh Climate Change Strategy and Action Plan (BCCSAP) 2.9 UN-REDD Programme 2.10 Synthesis of the Proposed Programmes and Initiatives for the Forest Sector of Bangladesh 2.11 Common Programmes, Policies and Practices Across Eight Initiatives 2.12 Potential Investment Options for the FIP 2.13 Linking of Proposed Actions under -
Indian Sundarbans Mangrove Forest
Biological Conservation 251 (2020) 108751 Contents lists available at ScienceDirect Biological Conservation journal homepage: www.elsevier.com/locate/biocon Review Indian Sundarbans mangrove forest considered endangered under Red List T of Ecosystems, but there is cause for optimism ⁎ Michael Sieversa, , Mahua Roy Chowdhuryb, Maria Fernanda Adamea,c, Punyasloke Bhaduryd, Radhika Bhargavae, Christina Buelowa, Daniel A. Friesse, Anwesha Ghoshd, Matthew A. Hayesa, Eva C. McClurea, Ryan M. Pearsona, Mischa P. Turschwellc, Thomas A. Worthingtonf, Rod M. Connollya a Australian Rivers Institute – Coast and Estuaries, School of Environment and Science, Griffith University, Gold Coast, QLD 4222, Australia b Department of Marine Science, University of Calcutta, Kolkata 700 019, India c Australian Rivers Institute – Coast and Estuaries, School of Environment and Science, Griffith University, Nathan, QLD 4111, Australia d Centre for Climate and Environmental Studies and Integrative Taxonomy and Microbial Ecology Research Group, Department of Biological Sciences, Indian Institute of Science Education and Research Kolkata, Mohanpur, 741246, Nadia, West Bengal, India e Department of Geography, National University of Singapore, 117570, Singapore f Conservation Science Group, Department of Zoology, University of Cambridge, Cambridge CB2 3QZ, UK ARTICLE INFO ABSTRACT Keywords: Accurately evaluating ecosystem status is vital for effective conservation. The Red List of Ecosystems (RLE) from Ecosystem condition the International Union for the Conservation of Nature (IUCN) is the global standard for assessing the risk of Ecosystem integrity ecosystem collapse. Such tools are particularly needed for large, dynamic ecosystem complexes, such as the Ecosystem risk assessment Indian Sundarbans mangrove forest. This ecosystem supports unique biodiversity and the livelihoods of millions, Habitat assessment but like many mangrove forests around the world is facing substantial pressure from a range of human activities. -
A Review of Forest Policy Trends in Bangladesh ῌbangladesh Forest Policy Trendsῃ
Policy Trend Report ,**,: ++.-+,+ A Review of Forest Policy Trends in Bangladesh ῌBangladesh Forest Policy Trendsῌ Md. Millat-e-MUSTAFA Institute of Forestry and Environmental Sciences, University of Chittagong Abstract : Forest policy in Bangladesh has its origins in the nation’s colonial past and has a distinct commercial slant. The first formal forest policy to be enunciated in what was then British India came into e#ect in +23. and was characterized by the progressive commercialization of forest use for revenue maximization, expansion of agricultur- al land at the expense of forests for commercial farming, systematic alienation of local communities from forests, and the progressive diminution of their traditional rights. The Pakistani period of rule (+3.1ῌ+31+) witnessed the formation of two forest policies, in +3// and +30,. However, this period did not di#er much in essence from the colonial period, and was characterized by a similar trend towards commercialization and the consequent alienation of local communities. As such, local rights and demands remained ignored as before. Following a bloody insurgency war, Bangladesh surfaced as a sovereign state on the global map in +31+. The Government of Bangladesh adopted the first National Forest Policy in +313 with the objective of providing greater protection and placing greater emphasis on conservation of the country’s forest assets whilst concomitantly developing its rural and industrial economies. However, the policy largely ignored the crucial issue of community participation and, consequently, little changed in comparison to the traditional colonial-industrial approach to forestry. The current forest policy was introduced in +33. and represents the first shift towards recognition of the importance of people’s participation in forestry. -
Mapping Deforestation and Forest Degradation Patterns in Western Himalaya, Pakistan
remote sensing Technical Note Mapping Deforestation and Forest Degradation Patterns in Western Himalaya, Pakistan Faisal Mueen Qamer 1,2,*, Khuram Shehzad 1, Sawaid Abbas 3, MSR Murthy 1, Chen Xi 2, Hammad Gilani 1 and Birendra Bajracharya 1 1 International Centre for Integrated Mountain Development (ICIMOD), Kathmandu 44700, Nepal; [email protected] (K.S.); [email protected] (M.M.); [email protected] (H.G.); [email protected] (B.B.) 2 The Xinjiang Institute of Ecology and Geography (XIEG), Chinese Academy of Sciences (CAS), Urumqi 830011, China; [email protected] 3 Department of Land Surveying and Geo-Informatics, The Hong Kong Polytechnic University, Hong Kong, China; [email protected] * Correspondence: [email protected]; Tel.: +977-01-500-3222 Academic Editors: Rasmus Fensholt, Stephanie Horion, Torbern Tagesson, Martin Brandt, Parth Sarathi Roy and Prasad S. Thenkabail Received: 31 December 2015; Accepted: 12 April 2016; Published: 6 May 2016 Abstract: The Himalayan mountain forest ecosystem has been degrading since the British ruled the area in the 1850s. Local understanding of the patterns and processes of degradation is desperately required to devise management strategies to halt this degradation and provide long-term sustainability. This work comprises a satellite image based study in combination with national expert validation to generate sub-district level statistics for forest cover over the Western Himalaya, Pakistan, which accounts for approximately 67% of the total forest cover of the country. The time series of forest cover maps (1990, 2000, 2010) reveal extensive deforestation in the area. Indeed, approximately 170,684 ha of forest has been lost, which amounts to 0.38% per year clear cut or severely degraded during the last 20 years. -
References AFFORESTATION
AFFORESTATION Drawdown Technical Assessment References Agyeman, V. K., Marfo, K. A., Kasanga, K. R., Danso, E., Asare, A. B., Yeboah, O. M., & Agyeman, F. (2003). Revising the taungya plantation system: new revenue-sharing proposals from Ghana. Unasylva, 54(1), 40-43. Aide, T. M., Zimmerman, J. K., Pascarella, J. B., Rivera, L., & Marcano-Vega, H. (2000). Forest regeneration in a chronosequence of tropical abandoned pastures: implications for restoration ecology. Restoration ecology, 8(4), 328-338. Aide, T. M., Clark, M. L., Grau, H. R., López-Carr, D., Levy, M. A., Redo, D., ... & Muñiz, M. (2013). Deforestation and reforestation of Latin America and the Caribbean (2001–2010). Biotropica, 45(2), 262- 271. Baccini, A. G. S. J., Goetz, S. J., Walker, W. S., Laporte, N. T., Sun, M., Sulla-Menashe, D., ... & Houghton, R. A. (2012). Estimated carbon dioxide emissions from tropical deforestation improved by carbon-density maps. Nature Climate Change, 2(3), 182-185. Backéus, S., Wikström, P., & Lämås, T. (2005). A model for regional analysis of carbon sequestration and timber production. Forest ecology and management,216(1), 28-40. Balooni, K., (n.d.) Economics of wastelands afforestation in India, a review. New Forests 26, 101–136. doi:10.1023/A:1024494010538 Barford, C. C., Wofsy, S. C., Goulden, M. L., Munger, J. W., Pyle, E. H., Urbanski, S. P., ... & Moore, K. (2001). Factors controlling long-and short-term sequestration of atmospheric CO2 in a mid-latitude forest. Science, 294(5547), 1688-1691. Betts, R. A. (2000). Offset of the potential carbon sink from boreal forestation by decreases in surface albedo. -
Understanding and Mapping Shifting Cultivation Using the Case Study of West Garo Hills, India
land Article Farms or Forests? Understanding and Mapping Shifting Cultivation Using the Case Study of West Garo Hills, India Amit John Kurien 1,2,* , Sharachchandra Lele 1 and Harini Nagendra 3 1 Centre for Environment and Development, Ashoka Trust for Research in Ecology and the Environment (ATREE), Royal Enclave, Jakkur P. O., Bengaluru, Karnataka 560064, India 2 Manipal Academy of Higher Education (MAHE), Manipal, Karnataka 576104, India 3 School of Development, Azim Premji University, PES Institute of Technology Campus, Pixel Park, B Block, Electronics City, Hosur Road, Bengaluru, Karnataka 560100, India * Correspondence: [email protected]; Tel.: +91-80-23635555 Received: 27 June 2019; Accepted: 27 August 2019; Published: 29 August 2019 Abstract: Attempts to study shifting cultivation landscapes are fundamentally impeded by the difficulty in mapping and distinguishing shifting cultivation, settled farms and forests. There are foundational challenges in defining shifting cultivation and its constituent land-covers and land-uses, conceptualizing a suitable mapping framework, and identifying consequent methodological specifications. Our objective is to present a rigorous methodological framework and mapping protocol, couple it with extensive fieldwork and use them to undertake a two-season Landsat image analysis to map the forest-agriculture frontier of West Garo Hills district, Meghalaya, in Northeast India. We achieve an overall accuracy of ~80% and find that shifting cultivation is the most extensive land-use, followed by tree plantations -
State, Society and Timber Mafia in Forest Conservation
State, Society and Timber Mafia in Forest Conservation A research paper submitted by Usman Ashraf (Pakistan) in partial fulfillment of the requirements for obtaining the degree of Masters of Arts in Development Studies Specialization: Agrarian, Food and Environmental Studies (AFES) Members in the examining committee Prof. Dr. Saturnino M. Borras Dr. Julien-François Gerber The Hague, The Netherlands December, 2017 i Disclaimer This document represents part of the author’s study programme while at the Institute of Social Science. The views stated therein are those of the author and not necessarily those of the Institute. Inquiries: Postal address: Institute of Social Studies P. O. Box 29776 2502 LT The Hague The Netherlands Location: Kortenaerkade 12 2518 AX The Hague The Netherlands Telephone: +31 70 426 0460 Fax: +31 70 426 0799 ii Table of Contents Abstract ...................................................................................................................................... v List of Figures ........................................................................................................................... vi List of abbreviations and acronyms ........................................................................................vii Chapter 1 Introduction .............................................................................................................. 8 1.1 Introduction ............................................................................................................................................ -
State of the World's Forests 2016
2016 STATE OF THE WORLD’S FORESTS STATE STATE OF THE WORLD’S FORESTS 2016 FORESTS AND AGRICULTURE: LAND-USE FAO CHALLENGES AND OPPORTUNITIES COVER PHOTO ©FAO/Adi Wiratmo INDONESIA. Terraced rice fields on the island of Bali. In order to make the most of the land and prevent erosion, this terracing system maintains the ecosystem while providing a livelihood for local farmers. Recommended citation: FAO. 2016. State of the World’s Forests 2016. Forests and agriculture: land-use challenges and opportunities. Rome. The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. ISBN 978-92-5-109208-8 FAO encourages the use, reproduction and dissemination of material in this information product. Except where otherwise indicated, material may be copied, downloaded and printed for private study, research and teaching purposes, or for use in non-commercial products or services, provided that appropriate acknowledgement of FAO as the source and copyright holder is given and that FAO’s endorsement of users’ views, products or services is not implied in any way. -
International Illegal Logging: Background and Issues
February 26, 2019 International Illegal Logging: Background and Issues Background Country of Origin Estimated % of Illegal Logging Illegal logging is a pervasive problem throughout the world and generally is defined as the harvest, transport, purchase, Papua New Guinea 70% or sale of timber in violation of national laws. Illegal logging can lead to degraded forest ecosystems and loss of Peru 80%-90% biodiversity, impede economic development, challenge Republic of Congo 70% local governance, and contribute to crime and corruption. In regions with large tropical forests, such as the Amazon and 10%-15% in Northwest and 50% in Russian Federation areas in Central Africa and Southeast Asia, illegal logging Far East Russia. is estimated to account for 50%-90% of all forestry Sources: A. Hoare, Tackling Illegal Logging and the Related Trade, activities, according to the International Criminal Police Chatham House Report, July 2015; and World Bank, Strengthening Organization (INTERPOL). INTERPOL also reports that Forest Law Enforcement and Governance, August 2006. the trade in illegally harvested timber is between $51 billion and $152 billion annually. This figure does not take into The top consumers of international illegal logging include account the reduction in legal timber prices caused by China, India, Japan, the United States, and countries within illegal logging, which is estimated to be between 7% and the European Union (EU). 16%. Some express concern that U.S. demand for tropical timber from countries in Latin America and Southeast Asia U.S. Laws That Address Illegal Logging could, in part, drive illegal logging in those areas. The The United States has several laws that address aspects of United States is the world’s largest wood products international illegal logging. -
South Asian Forests and Forestry to 2020
RAP PUBLICATION 2012/10 ASIA-PACIFIC FORESTRY COMMISSION SOUTH ASIAN FORESTS AND FORESTRY TO 2020 SUBREGIONAL REPORT OF THE SECOND ASIA-PACIFIC FORESTRY SECTOR OUTLOOK STUDY FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS Bangkok, 2012 The designations employed and the presentation of material in this publication do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specifi c companies or products of manufacturers, whether or not these have been patented, does not imply that that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. All rights reserved. No part of this publication may be reproduced, stored in a retrieval system, or transmitted in any form or by any means, electronic, mechanical, photocopying or otherwise, without the prior permission of the copyright owner. Applications for such permission, with a statement of the purpose and extent of the reproduction, should be addressed to the Director, Information Division, Food and Agriculture Organization of the United Nations, Viale delle Terme di Caracalla, 00100 Rome, Italy. Cover design: Chanida Chavanich For copies, write to: Patrick B. Durst Senior Forestry Offi cer FAO Regional Offi ce for Asia and the Pacifi c 39 Phra Atit Road Bangkok 10200 Thailand Tel: (66-2) 697 4000 Fax: (66-2) 697 4445 E-mail: [email protected] Printed and published in Bangkok, Thailand.