Old-Growth Forests
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The Story About Understory Why Everyone on Bald Head Island Should Care
Bald Head Association 910-457-4676 • www.BaldHeadAssociation.com 111 Lighthouse Wynd • PO Box 3030, Bald Head Island, NC 28461 The Story About Understory Why Everyone on Bald Head Island Should Care Bald Head Island is truly unique. As a barrier island, it at ground level. Bald Head Island’s latitudinal position is bordered by the Atlantic Ocean and Cape Fear River. BHI has supports both northern and southern species of plants.” 14 miles of pristine beaches; 12,400 acres, of which 10,000 acres Important understory plants include vines, small plants and are protected; over 244 species of birds, including the bald eagle; trees, mosses, lichens and even weeds. All are needed to have and the North Carolina Forest Preserve of nearly 200 acres. a healthy forest habitat. Many extreme forces of nature that have helped shape this The BHIC explains, “Vines play an important role. The very special island include hurricane-force winds, salt water and vines and herbaceous plants intertwine, further developing the salt spray, flooding and drought. There is another force of nature structural integrity of the forest and forming pockets of vegetation that impacts BHI — humans — and with us, development. that provide a base for songbirds to build nests. The vines twist The Bald Head Association is mandated by its Covenants to around the canopy and are the secret to wind protection. These help sustain BHI by managing the buildout of homes and by vines actually weave together the canopy so blowing winds don’t managing vegetation trimming/removal, to help protect its penetrate through the top layer and keep homes, plants, and members’ property values. -
Dynamics and Disturbance in an Old-Growth Forest Remnant In
DYNAMICS AND DISTURBANCE IN AN OLD-GROWTH FOREST REMNANT IN WESTERN OHIO Thesis Submitted to The College of Arts and Sciences of the UNIVERSITY OF DAYTON In Partial Fulfillment of the Requirements for The Degree of Master of Science in Biology By Sean Michael Goins UNIVERSITY OF DAYTON Dayton, Ohio August, 2012 DYNAMICS AND DISTURBANCE IN AN OLD-GROWTH FOREST REMNANT IN WESTERN OHIO Name: Goins, Sean Michael APPROVED BY: __________________________________________ Ryan W. McEwan, Ph.D. Committee Chair Assistant Professor __________________________________________ M. Eric Benbow, Ph.D. Committee Member Assistant Professor __________________________________________ Mark G. Nielsen, Ph.D. Committee Member Associate Professor ii ABSTRACT DYNAMICS AND DISTURBANCE IN AN OLD-GROWTH FOREST REMNANT IN WESTERN OHIO Name: Goins, Sean Michael University of Dayton Advisor: Dr. Ryan W. McEwan Forest communities are dynamic through time, reacting to shifts in disturbance and climate regimes. A widespread community shift has been witnessed in many forests of eastern North America wherein oak (Quercus spp.) populations are decreasing while maple (Acer spp.) populations are increasing. Altered fire regimes over the last century are thought to be the primary driver of oak-to-maple community shifts; however, the influence of other non-equilibrium processes on this community shift remains under- explored. Our study sought to determine the community structure and disturbance history of an old-growth forest remnant in an area of western Ohio where fires were historically uncommon. To determine community structure, abundance of woody species was measured within 32 plots at 4 canopy strata and dendrochronology was used to determine the relative age-structure of the forest. -
A Short History of Canopy Biology
CHAPTER 23 Tarzan or Jane? A Short History of Canopy Biology Margaret D. Lowrnan Cirowing up in the midwestern United States I knew trees IPPII.I looped~firrzone bare branch to the next in the backyard red maple with, I believed, thp sp~6.d and graw (!fa monkey making its rounds. Like Kiling? Mowgli, I had the po~itio~zand strength tf tcach branch memorized. I learned how to rest my body comfortabb arrzong thp orduly boughs in order to have a clear view of my mother, small as an ant, tending I~Bgarden below. The branches I favored became burnishedjom rqeated scuings. In tim~I ident$ed with the monkey's world. I grew up to be a ~oologist. -Mark Mofett, Thc High Fronticr, 1993 Why Study the Treetops? E.O. Wilson called it "the last frontier" of biological rcscarch on thc planct (Wilson 1992). Andrrw Mitchell referred to its invisible inhabitants as "a ~vorldI could only dream of" (Mitchell 2001). Tom Lolrejoy confessed that "thc canopy rendered me the biologist's equivalent of Tantalus from the \.cry outsidc" (I,o\.r.joy 1995). And Stevc Sutton compared it to "Alice grows up" as canop); science n~o\.csfrom a scnsc of wonder to a reality of hypotheses (Sutton 2001). Nalini Nadklrni esclaimed about "trcc climbing for Lgrown-ups" (Nadkarni 2001) and I simply notcd, "hly career is not conventional. I climb trecs" (Lowman 1999). In 1985, thcsc six indi- viduals may ha1.e represented almost half of thc canopy scientists worldwidc. Today, only two decades later, thrrc arc scveral hundred explorers of Wilson's last frontier. -
Non-Timber Forest Products
Agrodok 39 Non-timber forest products the value of wild plants Tinde van Andel This publication is sponsored by: ICCO, SNV and Tropenbos International © Agromisa Foundation and CTA, Wageningen, 2006. All rights reserved. No part of this book may be reproduced in any form, by print, photocopy, microfilm or any other means, without written permission from the publisher. First edition: 2006 Author: Tinde van Andel Illustrator: Bertha Valois V. Design: Eva Kok Translation: Ninette de Zylva (editing) Printed by: Digigrafi, Wageningen, the Netherlands ISBN Agromisa: 90-8573-027-9 ISBN CTA: 92-9081-327-X Foreword Non-timber forest products (NTFPs) are wild plant and animal pro- ducts harvested from forests, such as wild fruits, vegetables, nuts, edi- ble roots, honey, palm leaves, medicinal plants, poisons and bush meat. Millions of people – especially those living in rural areas in de- veloping countries – collect these products daily, and many regard selling them as a means of earning a living. This Agrodok presents an overview of the major commercial wild plant products from Africa, the Caribbean and the Pacific. It explains their significance in traditional health care, social and ritual values, and forest conservation. It is designed to serve as a useful source of basic information for local forest dependent communities, especially those who harvest, process and market these products. We also hope that this Agrodok will help arouse the awareness of the potential of NTFPs among development organisations, local NGOs, government officials at local and regional level, and extension workers assisting local communities. Case studies from Cameroon, Ethiopia, Central and South Africa, the Pacific, Colombia and Suriname have been used to help illustrate the various important aspects of commercial NTFP harvesting. -
Strengthening Protection of Marojejy National Park
SPECIAL POINTS DECEMBER 2016 OF INTEREST: Vol. 5, No. 2 ñ Workshop for Forest GuiDes ñ Brief but Meaningful Conservaton news from the Sambava-Andapa-Vohemar-Antalaha region of NE Madagascar ñ WorlD Lemur Festival Strengthening Protecton of Marojejy Natonal Park INSIDE THIS by Charlie Welch ISSUE: Earlier this year DLC- Strengthening Protec- 1 tion of Marojejy Na- SAVA was fortunate to tional Park receive a grant from Workshop for Forest 3 Save Our Species (SOS) Guides to increase the Brief but Meaningful 4 protecton of Marojejy Natonal Park, in World Lemur Festival 8 collaboraton with “Climate Change and 9 Madagascar Natonal Lemurs” Workshop Parks (MNP). The grant Environmental Educa- 12 supports clearly tion Teacher Training establishing and marking DLC-SAVA “Lamba” 13 the boundary with Now Available! metallic signs to prevent First CURSA Gradua- 14 both intentonal and unintentonal intrusion into the park. Although DLC-SAVA had already tion includes Sylvio sponsored delineaton of certain priority sectons of the park boundary, extensive areas in Exploring Human and 15 remote parts of Marojejy remained unmarked. There was no way for local people to know Environmental Health exactly where the boundary was supposed to be. Agricultural land ofen extends right up to in the SAVA Region the boundary around much of the park, and if Duke Engineers in 18 the limit is not clear, burning and cultvaton SAVA can actually extend into the park. A clear Closing Comments 20 boundary also discourages other illegal actvites in the park, such as wood collecton and huntng. Teams of local people, organized by MNP, installed the signs, which were made in Andapa. -
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. -
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. -
Choosing a Forest Definition for the Clean Development Mechanism )$26 FORESTS and CLIMATE CHANGE WORKING PAPER 4
Forests and Climate Change Working Paper 4 Choosing a forest definition for the Clean Development Mechanism )$26 FORESTS AND CLIMATE CHANGE WORKING PAPER 4 CHOOSING A FOREST DEFINITION FOR THE CLEAN DEVELOPMENT MECHANISM Till Neeff Heiner von Luepke Dieter Schoene Table of Contents Abstract.................................................................................................................................................. 3 Forest, afforestation and reforestation as defined for the Clean Development Mechanism .......... 3 Remaining ambiguities of definitions .................................................................................... 4 Considering existing national definitions............................................................................... 5 Choosing parameter values .................................................................................................................. 6 Furthering national policy objectives with the CDM............................................................. 7 Accommodating prior site conditions .................................................................................... 7 Facilitating project types........................................................................................................ 9 Integrating prior site conditions and project types............................................................... 10 What parameter values have NAI countries selected up to the present? ............................. 12 Conclusions ......................................................................................................................................... -
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%). -
Sass Forestecomgt 2018.Pdf
Forest Ecology and Management 419–420 (2018) 31–41 Contents lists available at ScienceDirect Forest Ecology and Management journal homepage: www.elsevier.com/locate/foreco Lasting legacies of historical clearcutting, wind, and salvage logging on old- T growth Tsuga canadensis-Pinus strobus forests ⁎ Emma M. Sassa, , Anthony W. D'Amatoa, David R. Fosterb a Rubenstein School of Environment and Natural Resources, University of Vermont, Burlington, VT 05405, USA b Harvard Forest, Harvard University, 324 N Main St, Petersham, MA 01366, USA ARTICLE INFO ABSTRACT Keywords: Disturbance events affect forest composition and structure across a range of spatial and temporal scales, and Coarse woody debris subsequent forest development may differ after natural, anthropogenic, or compound disturbances. Following Compound disturbance large, natural disturbances, salvage logging is a common and often controversial management practice in many Forest structure regions of the globe. Yet, while the short-term impacts of salvage logging have been studied in many systems, the Large, infrequent natural disturbance long-term effects remain unclear. We capitalized on over eighty years of data following an old-growth Tsuga Pine-hemlock forests canadensis-Pinus strobus forest in southwestern New Hampshire, USA after the 1938 hurricane, which severely Pit and mound structures damaged forests across much of New England. To our knowledge, this study provides the longest evaluation of salvage logging impacts, and it highlights developmental trajectories for Tsuga canadensis-Pinus strobus forests under a variety of disturbance histories. Specifically, we examined development from an old-growth condition in 1930 through 2016 across three different disturbance histories: (1) clearcut logging prior to the 1938 hurricane with some subsequent damage by the hurricane (“logged”), (2) severe damage from the 1938 hurricane (“hurricane”), and (3) severe damage from the hurricane followed by salvage logging (“salvaged”). -
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. -
Understory Forest Monitoring: a Guide for Small Forest Managers
Understory Forest Monitoring: A Guide for Small Forest Managers With funding provided by BEFORE: A dense monoculture of invasive periwinkle (Vinca species). AFTER: A diverse mix of native vegetation beginning to establish. It will mature into a lush forest Á oor of native wildÁ owers. Managing a healthy forest is not just about having healthy trees. Foresters, scientists, and private woodland owners have an interest in what is growing on the forest Á oor. A healthy understory can offer: • Flowers for native pollinators • Food for wildlife • Resiliency against invasion by forest weeds • Organic material to build healthier soil • Stable soil that doesn’t erode into nearby streams • Beautiful views while recreating in the forest Just like taking inventory of the forest, measuring tree diameters and spacing, it is also important to monitor the changes over time on the forest Á oor. Herbaceous forest plants tend to reach their peak bloom and cover in mid to late spring (mid-May to mid-June in western Oregon). It’s best to monitor forest understory consistently at this time of year. There are dozens of ways to monitor the understory plants in a forest. Two effective methods are described here. Point intercept method This method is performed by laying out a straight line transect in the forest and documenting what is growing on the forest Á oor at one- foot increments along the transect. West Multnomah Soil & Water Conservation District often sets up multiple transects that are 33’ in length giving us 33 data points per transect. The data gathered from the plots can be used to À nd the average cover of different vegetation types in your forest.