Sustainable Forest Management
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Primary Forests: Definition, Status and Future Prospects for Global Conservation
This article was originally published in the Encyclopedia of the Anthropocene published by Elsevier, and the attached copy is provided by Elsevier for the author's benefit and for the benefit of the author’s institution, for non-commercial research and educational use including without limitation use in instruction at your institution, sending it to specific colleagues who you know, and providing a copy to your institution’s administrator. All other uses, reproduction and distribution, including without limitation commercial reprints, selling or licensing copies or access, or posting on open internet sites, your personal or institution’s website or repository, are prohibited. For exceptions, permission may be sought for such use through Elsevier's permissions site at: http://www.elsevier.com/locate/permissionusematerial Kormos C.F., Mackey B., DellaSala D.A., Kumpe N., Jaeger T., Mittermeier R.A. and Filardi C. (2018) Primary Forests: Definition, Status and Future Prospects for Global Conservation. In: Dominick A. DellaSala, and Michael I. Goldstein (eds.) The Encyclopedia of the Anthropocene, vol. 2, p. 31-41. Oxford: Elsevier. © 2018 Elsevier Inc. All rights reserved. Author's personal copy Primary Forests: Definition, Status and Future Prospects for Global Conservation CF Kormos, WILD Foundation, Boulder, CO, United States; Conservation International, Arlington, VA, United States B Mackey, Griffith University, Nathan, QLD, Australia DA DellaSala, Geos Institute, Ashland, Oregon, United States N Kumpe, Zoological Society of London, London, United Kingdom T Jaeger, International Union for Conservation of Nature, Gland, Switzerland RA Mittermeier and C Filardi, Conservation International, Arlington, VA, United States © 2018 Elsevier Inc. All rights reserved. Photo: Cristina Mittermeier What Is a Primary Forest? Earth has lost about 35% of its preagricultural forest over centuries. -
FORESTRY SECTOR POLICY GOAL, OBJECTIVES and STRATEGIES
National Forest Policy, Timor-Leste, December 2005 SUPPORT for the FORMULATION of a NATIONAL FOREST POLICY STATEMENT – TIMOR LESTE FORESTRY SECTOR POLICY GOAL, OBJECTIVES and STRATEGIES Introduction The National Development Plan (2002) assigns the Ministry of Agriculture, Fisheries and Forestry (MAFF) as the Government agency having prime responsibility for forestry development. New law defined the Ministry’s mandate and structure in 2002. The National Directorate of Coffee and Forestry (NDCF) is one of three national directorates within the ministry and has broad responsibilities for community forestry, watershed management, forest protection, plantation forestry, protected natural areas development and other aspects of forestry development. The National Development Plan emphasises a sustainable approach to the development and management of the forest resources of the country. It recognizes that forests are important for their biological diversity and that forest conservation is a priority task in forest development planning. National development strategies recognise the limited ability of NDCF to support field programmes and it asserts that they will mainly focus on improving that capability and assist in providing the basic steps that will enable the NDCF to work towards achieving the national objective of sustainable forest management. The strategies also attempt to make a contribution to other relevant Government short-term objectives, such as rural poverty alleviation. The NDCF will make a major contribution towards combating deforestation and forest degradation by initiating, in close cooperation with other sections of MAFF, a series of integrated programmes that will closely involve rural communities. Emphasis will be placed on reducing the adverse effects of shifting cultivation and other pressures on forests and encouraging the participation of communities to protect forests and watersheds. -
Forest Management Planning
Forest Management Planning Basic knowledge Welcome to the Forest Management Planning Module. This module is intended for forest owners and managers wishing to plan SFM activities and to enable monitoring and control. The module provides information and links to tools and case studies, to guide users in planning the implementation of SFM at the forest management unit level. Forest management is the process of planning and implementing practices for the stewardship and use of forests and other wooded land targeted at specific environmental, economic, social and cultural objectives. Forest management planning is a fundamental component of SFM, and it may be required at various scales, from local to national; this module focuses on the local (or forest management unit) scale. The role of forest management planning is to determine and express the objectives of forest management in a specified area of forest and to set out the steps to be taken to achieve those objectives. Forest management planning is important for many reasons. For example, it can: help forest owners and managers identify what they want from the forest and provide an efficient course of action to meet those objectives; provide a means by which stakeholders can participate in forest management and ensure clarity on the roles and responsibilities of the various stakeholders; ensure the existence and functionality of the resource while also increasing its value (e.g. specifying where, how and under what conditions and constraints the resource may be used); save time and reduce costs (e.g. in road construction and wood harvesting); reduce risks and their impacts and avoid potentially costly forest management mistakes (e.g. -
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. -
Fifth World Forestry Congress
Proceedings of the Fifth World Forestry Congress VOLUME 1 RE University of Washington, Seattle, Washington United States of America August 29September 10, 1960 The President of the United States of America DWIGHT D. EISENHOWER Patron Fifth World Forestry Congress III Contents VOLUME 1 Page Chapter1.Summary and Recommendations of the Congress 1 Chapter 2.Planning for the Congress 8 Chapter3.Local Arrangements for the Congress 11 Chapter 4.The Congress and its Program 15 Chapter 5.Opening Ceremonies 19 Chapter6. Plenary Sessions 27 Chapter 7.Special Congress Events 35 Chapitre 1.Sommaire et recommandations du Congrès 40 Chapitre 2.Preparation des plans en vue du Congrès 48 Chapitre 3.Arrangements locaux en vue du Congrès 50 Chapitre 4.Le Congrès et son programme 51 Chapitre 5.Cérémonies d'ouverture 52 Chapitre 6.Seances plénières 59 Chapitre 7.Activités spéciales du Congrès 67 CapItullo1. Sumario y Recomendaciones del Congreso 70 CapItulo 2.Planes para el Congreso 78 CapItulo 3.Actividades Locales del Congreso 80 CapItulo 4.El Congreso y su Programa 81 CapItulo 5.Ceremonia de Apertura 81 CapItulo 6.Sesiones Plenarias 88 CapItulo 7.Actos Especiales del Congreso 96 Chapter8. Congress Tours 99 Chapter9.Appendices 118 Appendix A.Committee Memberships 118 Appendix B.Rules of Procedure 124 Appendix C.Congress Secretariat 127 Appendix D.Machinery Exhibitors Directory 128 Appendix E.List of Financial Contributors 130 Appendix F.List of Participants 131 First General Session 141 Multiple Use of Forest Lands Utilisation multiple des superficies boisées Aprovechamiento Multiple de Terrenos Forestales Second General Session 171 Multiple Use of Forest Lands Utilisation multiple des superficies boisées Aprovechamiento Multiple de Terrenos Forestales Iv Contents Page Third General Session 189 Progress in World Forestry Progrés accomplis dans le monde en sylviculture Adelantos en la Silvicultura Mundial Section I.Silviculture and Management 241 Sessions A and B. -
Tropical Timber: a Guide to Responsible Sourcing and Financing
TROPICAL TIMBER: A GUIDE TO RESPONSIBLE SOURCING AND FINANCING 1 1 | WHY IS PRESERVING FORESTS SO IMPORTANT? 4 | WHAT ARE THE ESG RISKS POSED BY UNSUSTAINABLE | TIMBER AND PULP PRODUCTION? 8 | MINIMISING RISK: A ROLE FOR VOLUNTARY | SUSTAINABILITY AND LEGALITY CERTIFICATION? 12 | KEY QUESTIONS THAT FINANCIAL INSTITUTIONS | AND BUYERS SHOULD BE ASKING 14 | IDENTIFYING RISKS AND OPPORTUNITIES 18 | CALL TO ACTION WHY IS PRESERVING FORESTS SO IMPORTANT? Tropical forests are estimated to house eighty percent of terrestrial biodiversity on earth,1 they regulate global rainfall, and provide a home, livelihoods and cultural functions to over 70 million Indigenous and forest-dependent peoples.2 They also store vast quantities of carbon, One of the most significant has been “locking in” a key greenhouse gas in the rapid expansion of agri-commodities vegetation and nutrient-rich forest soils. including oil palm in Southeast Asia5 and It is estimated that around 250 billion tonnes cattle ranching and soybean production in of carbon are stored in tropical forest above- South America.6 The degradation of tropical ground biomass alone, equating to roughly forests has received far less public attention 90 years of global fossil fuel emissions at than deforestation, despite also having today’s levels.3 However, growing recognition significant negative impacts on ecosystem of the importance of tropical forests comes function and biodiversity.7 The key driver at a time when forests are increasingly under of degradation is unsustainable logging threat from unsustainable production of practices, but degradation can also be forest-risk commodities including palm oil, caused by natural occurrences such as fire, beef, soy, timber and natural rubber. -
Old-Growth Forests
Pacific Northwest Research Station NEW FINDINGS ABOUT OLD-GROWTH FORESTS I N S U M M A R Y ot all forests with old trees are scientifically defined for many centuries. Today’s old-growth forests developed as old growth. Among those that are, the variations along multiple pathways with many low-severity and some Nare so striking that multiple definitions of old-growth high-severity disturbances along the way. And, scientists forests are needed, even when the discussion is restricted to are learning, the journey matters—old-growth ecosystems Pacific coast old-growth forests from southwestern Oregon contribute to ecological diversity through every stage of to southwestern British Columbia. forest development. Heterogeneity in the pathways to old- growth forests accounts for many of the differences among Scientists understand the basic structural features of old- old-growth forests. growth forests and have learned much about habitat use of forests by spotted owls and other species. Less known, Complexity does not mean chaos or a lack of pattern. Sci- however, are the character and development of the live and entists from the Pacific Northwest (PNW) Research Station, dead trees and other plants. We are learning much about along with scientists and students from universities, see the structural complexity of these forests and how it leads to some common elements and themes in the many pathways. ecological complexity—which makes possible their famous The new findings suggest we may need to change our strat- biodiversity. For example, we are gaining new insights into egies for conserving and restoring old-growth ecosystems. canopy complexity in old-growth forests. -
Managing for Late-Successional/Old-Growth Characteristics in Northern Hardwood-Conifer Forests William S
Forest Ecology and Management 235 (2006) 129–142 www.elsevier.com/locate/foreco Managing for late-successional/old-growth characteristics in northern hardwood-conifer forests William S. Keeton * Rubenstein School of Environment and Natural Resources, University of Vermont, Burlington, VT 05405, United States Received 19 March 2006; received in revised form 2 August 2006; accepted 2 August 2006 Abstract In the northern hardwood region of North America managing for late-successional forest habitats and functions is an important element of ecosystem management. This study tests the hypothesis that uneven-aged practices can be modified to accelerate rates of late-successional forest development. An approach, termed ‘‘structural complexity enhancement’’ (SCE), is compared against conventional uneven-aged systems modified to increase post-harvest structural retention. Experimental treatments, including controls, were applied to 2 ha units and replicated at two multi- aged northern hardwood forests in Vermont, USA. Structural objectives include vertically differentiated canopies, elevated large snag and downed log densities, variable horizontal density (including small gaps), and re-allocation of basal area to larger diameter classes. The latter objective is achieved, in part, by cutting to a rotated sigmoid diameter distribution. This is generated from a basal area (34 m2 haÀ1) and tree size (90 cm dbh) indicative of old-growth structure. Forest structure data have been collected over 2 years pre-treatment and 3 years post-treatment. Fifty-year simulations of stand development were run in NE-TWIGS and FVS comparing treatment and no treatment scenarios. Simulations also tested the sensitivity of large tree development to prescription parameters. Leaf area index retention was spatially variable but significantly (P < 0.001) greater under SCE (91%) compared to conventional treatments (75%). -
Forest Ecology and Management 267 (2012) 271-283
Forest Ecology and Management 267 (2012) 271-283 Contents lists available at SciVerse ScienceDirect Forest Ecology and Management journal hom epage: www.elsevier.com/locate/foreco Analyzing wildfire exposure and source-sink relationships on a fire prone forest landscape a, a b c Alan A. Ager *, Nicole M. Vaillant , Mark A. Finney , Haiganoush K. Preisler a USDA Forest Service, Pacific Northwest Research Station, Western Wildland Environmental Threat Assessment Center, 3160 NE 3rd Street, Prineville, OR 97754, USA b USDA Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory, 5775 Hwy. 10 West, Missoula, MT 59808, USA C USDA Forest Service, Pacific Southwest Research Station, 800 Buchannan Street, Albany, CA 9471 0, USA ARTICLE INFO ABSTR ACT Article history: We used simulation modeling to analyze wildfire exposure to social and ecological values on a 0,6 mil Received 9 August 2011 lion ha national forest in central Oregon, USA. We simulated 50,000 wildfires that replicated recent fire Received in revised form 13 November 2011 events in the area and generated detailed maps of burn probability (BP) and fire intensity distributions. Accepted 14 November 2011 We also recorded the ignition locations and size of each simulated fire and used these outputs to con Available online 8 January 2012 struct a fire source-sink ratio as the ratio of fire size to burn probability. Fire behavior was summarized for federal land management designations, including biological conservation reserves, recreational sites, Keywords: managed forest, and wildland urban interface. Burn probability from the simulations ranged from Wildfire simulation Wildfire risk 0.00091 to 0.026 within the study area (mean = 0.0023), and exhibited substantial variation among Conservation biology and within land designations. -
Forestry Study Guide
Forestry Study Guide Learning Objectives: Students should be able to: 1. Identify common trees without a key. 2. Identify specific or unusual species of trees or shrubs through the use of a key. 3. Understand how wildlife habitat relates to: forest communities, forest species, forest age structure, snags and den trees, availability of food and cover, and riparian zones. 4. Understand basic forest management concepts. 5. Be familiar with use of a diameter tape and other forestry tools. 6. Understand the benefits of trees in urban/suburban settings and the factors affecting their health and survival. Key Topics 1. Basic Forestry Knowledge; such as tree identification, silvics of common trees, tree measurement and tool use, and interaction of forests and environment. 2. Forest Ecology; such as the observation and identification of forest types, observing and describing forest stand structure, observing and describing site variables that affect tree species, and observing and identifying the stages of forest succession. 3. Silviculture Systems - such as describing the difference between harvesting and silvicultural systems, describe the difference between the goal of thinning and final harvest, describe the purpose of common silvicultural systems, and describe the management practices and their purpose. 4. Viewing Ecosystems; such as the observation of how trees and forests impact soil development, wildlife habitat, public places, agriculture, and on water quality. 5. Urban Forestry; such as the recognition of the value of trees in the urban landscape, choosing the correct species for specific locations, energy conservation through three plantings, urban wildlife benefits from tree plantings methods, proper tree care and maintenance, including wise choices in pest and disease control. -
Over 200 Top US Climate and Forest Scientists Urge
For Immediate Release Over 200 Top U.S. Climate and Forest Scientists Urge Congress: Protect Forests to Mitigate Climate Crisis 13 May 2020 Contact: William Moomaw, Ph.D. ([email protected]; 617-335-3994) Chad Hanson, Ph.D. ([email protected]; 530-273-9290) Dominick DellaSala, Ph.D. ([email protected]; 541-621-7223) As multiple current legislative proposals attempt to shoehorn measures that would increase logging, or increase funding for logging, into COVID-19 stimulus packages, over 200 top U.S. climate and forest scientists are now asking Congressional leaders to avoid using the pandemic emergency as a means for stripping away forest protections and promoting logging. In a historic and unprecedented letter sent to Congress today, the scientists conclude that, in order to avoid the worst impacts of the climate crisis, moving beyond fossil fuel consumption is not enough, and we must also increase forest protections and shift away from energy-intensive and greenhouse-gas polluting wood consumption. The scientists note that annual carbon emissions from logging in U.S. forests are comparable to emissions from the residential and commercial sectors combined. They ask legislators to reject false climate solutions that promote forest biomass logging (removal and incineration of trees for energy production) under the guise of “climate-friendly” or “carbon neutral” energy or logging for cross-laminated timber (CLT) and other wood products under the guise of carbon storage. Most of the carbon in trees is removed from forests when they are logged and quickly ends up in the atmosphere or in landfills, they caution. The scientists also note that logging, including commercial “thinning,” can often increase fire intensity in forests, while damaging soils and removing vital nutrients, which undermines the carbon sequestration and storage capacity of forests. -
Forest Stewardship Series 3: Forest Ecology
PUBLICATION 8233 FOREST STEWARDSHIP SERIES 3 Forest Ecology LAURIE LITMAN, InfoWright, Stockton, CA; GARY NAKAMURA, UCCE Forestry Specialist, Department of Environmental Science, Policy, and Management, University of California, Berkeley A forest is more than trees. It is also the shrubs, wildflowers, and grasses; the animals that depend on and live among these plants; the soil in which the plants grow; the UNIVERSITY OF dead trees and plants; the stream that flows through it; the insects, fungi, bacteria, CALIFORNIA and organisms you cannot readily see; and the climate. In short, a forest is an eco- Division of Agriculture system. An ecosystem is simply a specific area of the earth that includes all the liv- and Natural Resources ing organisms and nonliving components of the environment that interact within its http://anrcatalog.ucdavis.edu boundaries. An ecosystem can be any size, such as a log, pond, field, forest, or the whole earth’s biosphere. Objective It is useful to understand and manage your forest as an ecosystem Understand the structure and because all the components influence one another: for example, if you functions of forested ecosystems want certain tree species in your forest, you may have to manage the in California. competing vegetation. You cannot control certain aspects of the ecosys- tem such as climate; you must learn to live within its constraints of Competencies temperature and precipitation. In many cases the dates of last and first • Identify the forest ecosystem(s) on your frost control the growing season, the types of plants you can grow, and property. the productivity of your forest.