The Effect of Alternative Forest Management Models on the Forest Harvest and Emissions As Compared to the Forest Reference Level
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Protect Us from Climate Change
INTRODUCTION This project documents both the existing value and potential of New England’s working forest lands: Value – not only in terms of business opportunities, jobs and income – but also nonfinancial values, such as enhanced wildlife populations, recreation opportunities and a healthful environment. This project of the New England Forestry Foundation (NEFF) is aimed at enhancing the contribution the region’s forests can make to sustainability, and is intended to complement other efforts aimed at not only conserving New England’s forests, but also enhancing New England’s agriculture and fisheries. New England’s forests have sustained the six-state region since colonial settlement. They have provided the wood for buildings, fuel to heat them, the fiber for papermaking, the lumber for ships, furniture, boxes and barrels and so much more. As Arizona is defined by its desert landscapes and Iowa by its farms, New England is defined by its forests. These forests provide a wide range of products beyond timber, including maple syrup; balsam fir tips for holiday decorations; paper birch bark for crafts; edibles such as berries, mushrooms and fiddleheads; and curatives made from medicinal plants. They are the home to diverse and abundant wildlife. They are the backdrop for hunting, fishing, hiking, skiing and camping. They also provide other important benefits that we take for granted, including clean air, potable water and carbon storage. In addition to tangible benefits that can be measured in board feet or cords, or miles of hiking trails, forests have been shown to be important to both physical and mental health. Beyond their existing contributions, New England’s forests have unrealized potential. -
Forest Dieback/Damages in European State Forests and Measures to Combat It Several EUSTAFOR Members Have Recently Experienced An
Forest dieback/damages in European State Forests and measures to combat it Several EUSTAFOR members have recently experienced and reported on severe cases of forest dieback, caused by different biotic and abiotic agents. To get a better overview of these events and their consequences, with a view to a possible exchange of experiences among EUSTAFOR members as well as the development of proposals on how to communicate on these issues, the EUSTAFOR Office sent a short questionnaire to SFMOs in Europe. What follows is a comprehensive summary of the key information we received from our members. Results Out of 19 responses, 17 experienced forest dieback/damage to their forests. Only Romania and Ireland reported no forest dieback. However, Coillte (Ireland) is experiencing the problem with certain species, so they answered accordingly. Due to EUSTAFOR’s membership structure in some countries, we received input from more than one organization in that country. For example, in Germany, five different regional forest enterprises responded to the survey and, in Bulgaria, information came from two sources: the governing body - Executive Forest Agency (Ministry of Agriculture and Foods) and from one of the regional forestry enterprises. The reporting period relates to the most current available data. For the majority of the reports, this is 2018-2019. A few members, however, reported data that is a bit older. Figure 1: Map of members that answered the survey European State Forest Association AISBL Phone: +32 (0)2 239 23 00 European Forestry House Fax: +32 (0)2 219 21 91 Rue du Luxembourg 66 www.eustafor.eu 1000 Brussels, Belgium VAT n° BE 0877.545. -
Agriculture, Forestry, and Other Human Activities
4 Agriculture, Forestry, and Other Human Activities CO-CHAIRS D. Kupfer (Germany, Fed. Rep.) R. Karimanzira (Zimbabwe) CONTENTS AGRICULTURE, FORESTRY, AND OTHER HUMAN ACTIVITIES EXECUTIVE SUMMARY 77 4.1 INTRODUCTION 85 4.2 FOREST RESPONSE STRATEGIES 87 4.2.1 Special Issues on Boreal Forests 90 4.2.1.1 Introduction 90 4.2.1.2 Carbon Sinks of the Boreal Region 90 4.2.1.3 Consequences of Climate Change on Emissions 90 4.2.1.4 Possibilities to Refix Carbon Dioxide: A Case Study 91 4.2.1.5 Measures and Policy Options 91 4.2.1.5.1 Forest Protection 92 4.2.1.5.2 Forest Management 92 4.2.1.5.3 End Uses and Biomass Conversion 92 4.2.2 Special Issues on Temperate Forests 92 4.2.2.1 Greenhouse Gas Emissions from Temperate Forests 92 4.2.2.2 Global Warming: Impacts and Effects on Temperate Forests 93 4.2.2.3 Costs of Forestry Countermeasures 93 4.2.2.4 Constraints on Forestry Measures 94 4.2.3 Special Issues on Tropical Forests 94 4.2.3.1 Introduction to Tropical Deforestation and Climatic Concerns 94 4.2.3.2 Forest Carbon Pools and Forest Cover Statistics 94 4.2.3.3 Estimates of Current Rates of Forest Loss 94 4.2.3.4 Patterns and Causes of Deforestation 95 4.2.3.5 Estimates of Current Emissions from Forest Land Clearing 97 4.2.3.6 Estimates of Future Forest Loss and Emissions 98 4.2.3.7 Strategies to Reduce Emissions: Types of Response Options 99 4.2.3.8 Policy Options 103 75 76 IPCC RESPONSE STRATEGIES WORKING GROUP REPORTS 4.3 AGRICULTURE RESPONSE STRATEGIES 105 4.3.1 Summary of Agricultural Emissions of Greenhouse Gases 105 4.3.2 Measures and -
Status and Development of Old-Growth Elements and Biodiversity During Secondary Succession of Unmanaged Temperate Forests
Status and development of old-growth elementsand biodiversity of old-growth and development Status during secondary succession of unmanaged temperate forests temperate unmanaged of succession secondary during Status and development of old-growth elements and biodiversity during secondary succession of unmanaged temperate forests Kris Vandekerkhove RESEARCH INSTITUTE NATURE AND FOREST Herman Teirlinckgebouw Havenlaan 88 bus 73 1000 Brussel RESEARCH INSTITUTE INBO.be NATURE AND FOREST Doctoraat KrisVDK.indd 1 29/08/2019 13:59 Auteurs: Vandekerkhove Kris Promotor: Prof. dr. ir. Kris Verheyen, Universiteit Gent, Faculteit Bio-ingenieurswetenschappen, Vakgroep Omgeving, Labo voor Bos en Natuur (ForNaLab) Uitgever: Instituut voor Natuur- en Bosonderzoek Herman Teirlinckgebouw Havenlaan 88 bus 73 1000 Brussel Het INBO is het onafhankelijk onderzoeksinstituut van de Vlaamse overheid dat via toegepast wetenschappelijk onderzoek, data- en kennisontsluiting het biodiversiteits-beleid en -beheer onderbouwt en evalueert. e-mail: [email protected] Wijze van citeren: Vandekerkhove, K. (2019). Status and development of old-growth elements and biodiversity during secondary succession of unmanaged temperate forests. Doctoraatsscriptie 2019(1). Instituut voor Natuur- en Bosonderzoek, Brussel. D/2019/3241/257 Doctoraatsscriptie 2019(1). ISBN: 978-90-403-0407-1 DOI: doi.org/10.21436/inbot.16854921 Verantwoordelijke uitgever: Maurice Hoffmann Foto cover: Grote hoeveelheden zwaar dood hout en monumentale bomen in het bosreservaat Joseph Zwaenepoel -
Non-Timber Forest Products and Their Contribution to Households Income
Suleiman et al. Ecological Processes (2017) 6:23 DOI 10.1186/s13717-017-0090-8 RESEARCH Open Access Non-timber forest products and their contribution to households income around Falgore Game Reserve in Kano, Nigeria Muhammad Sabiu Suleiman1*, Vivian Oliver Wasonga1, Judith Syombua Mbau1, Aminu Suleiman2 and Yazan Ahmed Elhadi1 Abstract Introduction: In the recent decades, there has been growing interest in the contribution of non-timber forest products (NTFPs) to livelihoods, development, and poverty alleviation among the rural populace. This has been prompted by the fact that communities living adjacent to forest reserves rely to a great extent on the NTFPs for their livelihoods, and therefore any effort to conserve such resources should as a prerequisite understand how the host communities interact with them. Methods: Multistage sampling technique was used for the study. A representative sample of 400 households was used to explore the utilization of NTFPs and their contribution to households’ income in communities proximate to Falgore Game Reserve (FGR) in Kano State, Nigeria. Descriptive statistics and logistic regression analysis were used to analyze and summarize the data collected. Results: The findings reveal that communities proximate to FGR mostly rely on the reserve for firewood, medicinal herbs, fodder, and fruit nuts for household use and sales. Income from NTFPs accounts for 20–60% of the total income of most (68%) of the sampled households. The utilization of NTFPs was significantly influenced by age, sex, household size, main occupation, distance to forest and market. Conclusions: The findings suggest that NTFPs play an important role in supporting livelihoods, and therefore provide an important safety net for households throughout the year particularly during periods of hardship occasioned by drought. -
Current Issues in Non-Timber Forest Products Research
New Cover 6/24/98 9:56 PM Page 1 Current Issues in Non-Timber Forest Products Research Edited by M. Ruiz Pérez and J.E.M. Arnold CIFOR CENTER FOR INTERNATIONAL FORESTRY RESEARCH Front pages 6/24/98 10:02 PM Page 1 CURRENT ISSUES IN NON-TIMBER FOREST PRODUCTS RESEARCH Front pages 6/24/98 10:02 PM Page 3 CURRENT ISSUES IN NON-TIMBER FOREST PRODUCTS RESEARCH Proceedings of the Workshop ÒResearch on NTFPÓ Hot Springs, Zimbabwe 28 August - 2 September 1995 Editors: M. Ruiz PŽrez and J.E.M. Arnold with the assistance of Yvonne Byron CIFOR CENTER FOR INTERNATIONAL FORESTRY RESEARCH Front pages 6/24/98 10:02 PM Page 4 © 1996 by Center for International Forestry Research All rights reserved. Published 1996. Printed in Indonesia Reprinted July 1997 ISBN: 979-8764-06-4 Cover: Children selling baobab fruits near Hot Springs, Zimbabwe (photo: Manuel Ruiz PŽrez) Center for International Forestry Research Bogor, Indonesia Mailing address: PO Box 6596 JKPWB, Jakarta 10065, Indonesia Front pages 6/24/98 10:02 PM Page 5 Contents Foreword vii Contributors ix Chapter 1: Framing the Issues Relating to Non-Timber Forest Products Research 1 J.E. Michael Arnold and Manuel Ruiz PŽrez Chapter 2: Observations on the Sustainable Exploitation of Non-Timber Tropical Forest Products An EcologistÕs Perspective Charles M. Peters 19 Chapter 3: Not Seeing the Animals for the Trees The Many Values of Wild Animals in Forest Ecosystems 41 Kent H. Redford Chapter 4: Modernisation and Technological Dualism in the Extractive Economy in Amazonia 59 Alfredo K.O. -
FAO Forestry Paper 120. Decline and Dieback of Trees and Forests
FAO Decline and diebackdieback FORESTRY of tretreess and forestsforests PAPER 120 A globalgIoia overviewoverview by William M. CieslaCiesla FADFAO Forest Resources DivisionDivision and Edwin DonaubauerDonaubauer Federal Forest Research CentreCentre Vienna, Austria Food and Agriculture Organization of the United Nations Rome, 19941994 The designations employedemployed and the presentation of material inin thisthis publication do not imply the expression of any opinion whatsoever onon the part ofof thethe FoodFood andand AgricultureAgriculture OrganizationOrganization ofof thethe UnitedUnited Nations concerning the legallega! status ofof anyany country,country, territory,territory, citycity oror area or of itsits authorities,authorities, oror concerningconcerning thethe delimitationdelimitation ofof itsits frontiers or boundarboundaries.ies. M-34M-34 ISBN 92-5-103502-492-5-103502-4 All rights reserved. No part of this publicationpublication may be reproduced,reproduced, stored in aa retrieval system, or transmittedtransmitted inin any form or by any means, electronic, mechani-mechani cal, photocopying or otherwise, without the prior permission of the copyrightownecopyright owner.r. Applications for such permission, withwith aa statement of the purpose andand extentextent ofof the reproduction,reproduction, should bebe addressed toto thethe Director,Director, Publications Division,Division, FoodFood andand Agriculture Organization ofof the United Nations,Nations, VVialeiale delle Terme di Caracalla, 00100 Rome, Italy.Italy. 0© FAO FAO 19941994 -
XIX DEVELOPMENT and CHARACTERISTICS of HIGH FOREST SYSTEMS I. DEVELOPMENT of SYSTEMS the Development of the Various Silvicultura
XIX DEVELOPMENT AND CHARACTERISTICS OF HIGH FOREST SYSTEMS I. DEVELOPMENT OF SYSTEMS THEdevelopment of the various silvicultural systems of the present day has been brought about by a combination of silvicultural con- siderations on the one hand and economic considerations on the other. The former relate to conditions of growth and regeneration, maintenance of soil-fertility, and protection against damage of various kinds; the latter take into account market or other demands, reduction of working costs, and other factors of an economic character. A study of the history of the various high forest systems affords interesting evidence as to how these systems have arisen. The selection system in its scientific form of to-day is of recent introduc- tion, although it arose from a primitive form of cutting dating from early times. Clear cutting has been practised for some centuries, at first with natural and later with artificial regeneration, but it was only in the beginning of last century that it was systematized in its present form by Cotta. The uniform system has been evolved during the last four centuries or more, although it was first applied in its present-day form by G. L. Hartig rather more than a century ago; there is little doubt that it arose from the now obsolete tire et aire system of France or from similar old systems of Germany. Group fellings were systematized by Gayer in the latter part of last century, although they had been practised many years before. The shelter-wood strip system, representing an important modern de- velopment, was adapted from the uniform system, while Wagner's BZendersaumschlag and the wedge system of Eberhard and Philipp are more recent modifications of the strip system. -
Structure and Management of Beech (Fagus Sylvatica L.) Forests in Italy
Review Article - doi: 10.3832/ifor0499-002 ©iForest – Biogeosciences and Forestry Collection: COST Action E52 Meeting 2008 - Florence (Italy) over the country. Evaluation of beech genetic resources for sustainable forestry Economic and social changes in the last Guest Editors: Georg von Wühlisch, Raffaello Giannini decades have brought about changes in the forestry sector in Italy, which, in turn, have impacted forests and forest management. Structure and management of beech (Fagus Beech forests have not been immune to these changes and in some ways represent an inter- sylvatica L.) forests in Italy esting case study on the changing perspect- ives of forest management in the face of changing environmental and socio economic Nocentini S conditions. This paper analyses the relationship Beech forests characterise the landscape of many mountain areas in Italy, from between stand structure and the management the Alps to the southern regions. This paper analyses the relationship between history of beech forests in Italy. The aim is stand structure and the management history of beech in Italy. The aim is to to outline possible strategies for the sustain- outline possible strategies for the sustainable management of these forest able management of these forest formations. formations. The present structure of beech forests in Italy is the result of many interacting factors. According to the National Forest Inventory, more than half Distribution of beech forests in the total area covered by beech has a long history of coppicing. High forests Italy cover 34% of the total beech area and 13% have complex structures which Beech forests are present in all the regions have not been classified in regular types. -
USGS DDS-43, Late Successional Old-Growth Forest Conditions
CHAPTER 6 Late Successional Old-Growth Forest Conditions ❆ CRITICAL FINDINGS ality, all forests are dynamic, although the rate and spatial distribution of change varies widely from region to region. Status of Current Late Successional Forests Late successional Under ideal conditions, Sierran trees may live from several old-growth forests of middle elevations (west-side mixed conifer, red centuries (common) to several thousand years (uncommon), fir, white fir, east-side mixed conifer, and east-side pine types) at depending on species. Changes in climate over the past 10,000 present constitute 7%–30% of the forest cover, depending on forest years (after the end of the Pleistocene) have resulted in a con- type. On average, national forests have about 25% the amount of tinuously changing mix of species aggregations. Fire, drought, the national parks, which is an approximate benchmark for pre-con- insect attacks, wind, avalanches, and other disturbances— tact forest conditions. East-side pine forests have been especially often in combination—have typically modified and not in- altered. frequently destroyed entire stands of trees. As seedling trees are added and other trees in a stand grow, mature, and even- Forest Simplification The primary impact of 150 years of forestry tually die, both the appearance and the ecological function of on middle-elevation conifer forests has been to simplify structure (in- the stand and the forest of which it is a part evolve until they cluding large trees, snags, woody debris of large diameter, canopies reach a condition we refer to as late successional. of multiple heights and closures, and complex spatial mosaics of veg- Old growth is incorporated within the broader category of etation), and presumably function, of these forests. -
Limiting the High Impacts of Amazon Forest Dieback with No-Regrets Science and Policy Action PERSPECTIVE David M
PERSPECTIVE Limiting the high impacts of Amazon forest dieback with no-regrets science and policy action PERSPECTIVE David M. Lapolaa,1, Patricia Pinhob, Carlos A. Quesadac, Bernardo B. N. Strassburgd,e, Anja Rammigf, Bart Kruijtg, Foster Brownh,i, Jean P. H. B. Omettoj, Adriano Premebidak, Jos ´eA. Marengol, Walter Vergaram, and Carlos A. Nobren Edited by B. L. Turner, Arizona State University, Tempe, AZ, and approved October 1, 2018 (received for review May 8, 2018) Large uncertainties still dominate the hypothesis of an abrupt large-scale shift of the Amazon forest caused by climate change [Amazonian forest dieback (AFD)] even though observational evidence shows the forest and regional climate changing. Here, we assess whether mitigation or adaptation action should be taken now, later, or not at all in light of such uncertainties. No action/later action would result in major social impacts that may influence migration to large Amazonian cities through a causal chain of climate change and forest degradation leading to lower river-water levels that affect transportation, food security, and health. Net-present value socioeconomic damage over a 30-year period after AFD is estimated between US dollar (USD) $957 billion (×109) and $3,589 billion (compared with Gross Brazilian Amazon Product of USD $150 bil- lion per year), arising primarily from changes in the provision of ecosystem services. Costs of acting now would be one to two orders of magnitude lower than economic damages. However, while AFD mitigation alternatives—e.g., curbing deforestation—are attainable (USD $64 billion), their efficacy in achieving a forest resilience that prevents AFD is uncertain. -
Forest Protection
FOREST PROTECTION Guide to Lectures Delivered at the Biltmore Forest School By C. A. SCHENCK, Ph. D. Director. 1909 The Inland Press, Asheville, N. C. PREFACE This book on “forest protection” is being printed, pre-eminently, for the benefit of the students attending the Biltmore Forest School. In American forestry, the most important duty of the forester consists of the suppression of forest fires. If forest fires were prevented, a second growth would follow invariable in the wake of a first growth removed by the forester or by the lumberman; and the problem of forest conservation would solve itself. If forest fires were prevented, a second growth would have a definite prospective value; and it would be worth while [sic] to treat it sylviculturally. If forest fires were prevented, our investments made in merchantable timber would be more secure; and there would be a lesser inducement for the rapid conversion of timber into cash. The issue of forest fires stands paramount in all forest protection. Compared with this issue, the other topics treated in the following passages dwindle down to insignificance. I write this with a knowledge of the fact that the leading timber firms in this country place an estimate of less than 1% on their annual looses of timber due to fires: These firms are operating close to their holdings; and if a tract is killed by fire the operations are swung over into the burned section as speedily as possible; and the salvage may amount to 99% of the timber burned. These firms do not pay any attention, in their estimate, to the “lucrum cessans,” nor to the prospective value of inferior trees, poles, saplings and seedlings.