12 Forests, Forest Management, and Protected Areas Chapter Objectives
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Forest Farming
Forest Farming Ken Mudge CY ROSE N NA Many sections of the Northeast have been reforested over the past century. Extensive forest cover is seen in this view from Wachu- sett Mountain in central Massachusetts. armers harvest crops from their fields, and agroforestry—a multidisciplinary approach to loggers harvest trees from their forests, agricultural production that achieves diverse, Fbut what do forest farmers harvest? The profitable, sustainable land use by integrating answer is an eclectic collection of non-timber trees with non-timber forest crops. forest crops like maple syrup, medicinal herbs, While some other agroforestry practices begin fruits, gourmet mushrooms, and nuts. with planting young trees that take years to Forest farming is an approach to forest man- mature, forest farming involves planting non- agement that combines some of the manage- timber forest crops beneath the canopy of an ment practices of conventional forestry with established forest. In other words, other agro- those of farming or gardening to achieve forestry practices bring the forest to the crops, an environmentally and economically sus- whereas forest farming brings the crops to the tainable land-use system. It is one of several forest. In this regard it is helpful to consider related practices that fall under the domain of the role of forest farming in overall forest man- Forest Farming 27 agement. A forest farm should be designed to bearing trees including walnuts and peaches, emulate as much as possible a natural forest. but there is no evidence of deliberate culti- This includes characteristics of a healthy forest vation of useful crops beneath the canopy of ecosystem such as species diversity, resilience established forest. -
Challenges of Governing Second-Growth Forests: a Case Study from the Brazilian Amazonian State of Pará
Forests 2014, 5, 1737-1752; doi:10.3390/f5071737 OPEN ACCESS forests ISSN 1999-4907 www.mdpi.com/journal/forests Article Challenges of Governing Second-Growth Forests: A Case Study from the Brazilian Amazonian State of Pará Ima Célia Guimarães Vieira 1,*, Toby Gardner 2,3, Joice Ferreira 4, Alexander C. Lees 1 and Jos Barlow 1,5 1 Museu Paraense Emilio Goeldi, Av. Magalhães Barata, 376, Belém, Pará, 66.040-170, Brazil; E-Mails: [email protected] (A.C.L.); josbarlow@gmail (J.B.) 2 Stockholm Environment Institute, Linnégatan 87 D, Box 24218, Stockholm, 10451, Sweden; E-Mail: [email protected] 3 Instituto International para Sustentabilidade, Estrada Dona Castorina, 124, Horto, Rio de Janeiro, RJ 22.460-320, Brazil 4 Embrapa Amazônia Oriental, Travessa Dr. Enéas Pinheiro s/n, CP 48, Belém, Pará, 66.095-100, Brazil; E-Mail: [email protected] 5 Lancaster Environment Centre, Lancaster University, Lancaster LA1 4YQ, UK * Author to whom correspondence should be addressed; E-Mail: [email protected]; Tel.: +55-91-3182-3247. Received: 11 April 2014; in revised form: 9 July 2014 / Accepted: 10 July 2014 / Published: 22 July 2014 Abstract: Despite the growing ecological and social importance of second-growth and regenerating forests across much of the world, significant inconsistencies remain in the legal framework governing these forests in many tropical countries and elsewhere. Such inconsistencies and uncertainties undermine attempts to improve both the transparency and sustainability of management regimes. Here, we present a case-study overview of some of the main challenges facing the governance of second-growth forests and the forest restoration process in the Brazilian Amazon, with a focus on the state of Pará, which is both the most populous state in the Amazon and the state with the highest rates of deforestation in recent years. -
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. -
The Effects of Postfire Salvage Logging on Aquatic Ecosystems in the American West
Forum The Effects of Postfire Salvage Logging on Aquatic Ecosystems in the American West JAMES R. KARR, JONATHAN J. RHODES, G. WAYNE MINSHALL, F. RICHARD HAUER, ROBERT L. BESCHTA, CHRISTOPHER A. FRISSELL, AND DAVID A. PERRY Recent changes in the forest policies, regulations, and laws affecting public lands encourage postfire salvage logging, an activity that all too often delays or prevents recovery. In contrast, the 10 recommendations proposed here can improve the condition of watersheds and aquatic ecosystems. Keywords: aquatic ecosystems, postfire salvage logging, public land management, salmonids, western forests hroughout the American West, a century of road hold moisture (Jenny 1980), with implications for soil bio- Tbuilding, logging, grazing, and other human activities has ta, plant growth (Rose et al. 2001, Brown et al. 2003), and degraded stream environments, causing significant losses of stream flow (Waring and Schlesinger 1985). Logging and associated roads carry a high risk of spreading nonindige- aquatic biodiversity and severe contractions in the range and nous, weedy species (CWWR 1996, Beschta et al. 2004). abundance of sensitive aquatic species, including native salmonid fishes (Rieman et al. 2003). Compounding these • Increased runoff and erosion alter river hydrology by increasing the frequency and magnitude of erosive high problems, federal land management has worsened ecological flows and raising sediment loads. These changes alter the degradation, rather than conserving or restoring forest eco- character of river channels and harm aquatic species rang- systems (Leopold 1937, Langston 1995, Hirt 1996). Land ing from invertebrates to fishes (Waters 1995). managers’ focus on commodity extraction—sharpened by re- • Construction and reconstruction of roads and landings cent changes in forest policy, regulations, and laws that en- (sites to which trees are brought, stacked, and loaded onto courage salvage logging after fires—perpetuates this trend and trucks) often accompany postfire salvage logging. -
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. -
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”). -
What Can Mixed‐Species Flock Movement Tell Us About the Value Of
BIOTROPICA 50(4): 664–673 2018 10.1111/btp.12557 What can mixed-species flock movement tell us about the value of Amazonian secondary forests? Insights from spatial behavior Karl Mokross1,2,3,5 , Jonathan R. Potts4, Cameron L. Rutt2,3, and Philip C. Stouffer2,3 1 Departamento de Ecologia, Universidade Estadual Paulista ‘Julio de Mesquita Filho’, Av. 24-A, 1515, Bela Vista, 13506-900 Rio Claro, SP, Brasil 2 School of Renewable Natural Resources, Louisiana State University, 227 RNR building, Baton Rouge, LA 70803-6202, USA 3 Biological Dynamics of Forest Fragments Project, Instituto Nacional de Pesquisas da Amazonia,^ Manaus 69011, Amazonas, Brazil 4 School of Mathematics and Statistics, University of Sheffield, G27c Hicks Building, Hounsfield Road, Sheffield, UK ABSTRACT The value of secondary forest for rain forest species remains an important question for conservation in the 21st century. Here, we describe the spatial behavior of understory mixed-species flocks in a heterogeneous landscape in central Amazonia. Understory mixed- species flocks represent a diverse, highly organized component of the rich Amazonian avifauna. We recorded movements within 26 flock home ranges in primary forest, secondary forest, interfaces between forest types, and forest fragments. We describe frequency and movement orientation in relation to forest edges, movement patterns and proportion of use between secondary and primary forest, the relation between home range sizes and vegetation height, and home range configuration. Flocks visited only a small portion of forest edges, and showed a tendency for moving parallel to edges next to less-developed secondary forest. Movement patterns in secondary forests did not show significant differences compared to primary forests. -
Tamm Review: Does Salvage Logging Mitigate Subsequent Forest Disturbances?
Forest Ecology and Management 481 (2021) 118721 Contents lists available at ScienceDirect Forest Ecology and Management journal homepage: www.elsevier.com/locate/foreco Tamm reviews Tamm review: Does salvage logging mitigate subsequent forest disturbances? Alexandro B. Leverkus a,b,*, Brian Buma c, Joseph Wagenbrenner d, Philip J. Burton e, Emanuele Lingua f, Raffaella Marzano g, Simon Thorn a a University of Würzburg, Rauhenebrach, Germany b Department of Ecology, University of Granada, Granada, Spain c University of Colorado, Denver, CO, USA d USDA Forest Service, Pacific Southwest Research Station, Arcata, CA, USA e University of Northern British Columbia, Terrace, B.C., Canada f University of Padova, Legnaro, PD, Italy g University of Torino, Grugliasco, TO, Italy ARTICLE INFO ABSTRACT Keywords: After natural forest disturbances such as wildfires, windstorms and insect outbreaks, salvage logging is Beetle outbreak commonly applied to reduce economic losses and mitigate subsequent disturbance risk. However, this practice is Compound disturbance controversial due to its potential ecological impacts, and its capacity to mitigate or increase the risk of subse- Disturbance interaction quent disturbances remains unclear. Salvage logging removes and alters the legacies remaining after natural Fire prevention disturbances, and it produces additional management legacies. Consequently, salvage logging has the potential Linked disturbance Pest control to alter the functional connection between natural disturbances and also produce new functional -
Afforestation and Reforestation - Michael Bredemeier, Achim Dohrenbusch
BIODIVERSITY: STRUCTURE AND FUNCTION – Vol. II - Afforestation and Reforestation - Michael Bredemeier, Achim Dohrenbusch AFFORESTATION AND REFORESTATION Michael Bredemeier Forest Ecosystems Research Center, University of Göttingen, Göttingen, Germany Achim Dohrenbusch Institute for Silviculture, University of Göttingen, Germany Keywords: forest ecosystems, structures, functions, biomass accumulation, biogeochemistry, soil protection, biodiversity, recovery from degradation. Contents 1. Definitions of terms 2. The particular features of forests among terrestrial ecosystems 3. Ecosystem level effects of afforestation and reforestation 4. Effects on biodiversity 5. Arguments for plantations 6. Political goals of afforestation and reforestation 7. Reforestation problems 8. Afforestation on a global scale 9. Planting techniques 10. Case studies of selected regions and countries 10.1. China 10.2. Europe 11. Conclusion Glossary Bibliography Biographical Sketches Summary Forests are rich in structure and correspondingly in ecological niches; hence they can harbour plentiful biological diversity. On a global scale, the rate of forest loss due to human interference is still very high, currently ca. 10 Mha per year. The loss is highest in the tropics; in some tropical regions rates are alarmingly high and in some virtually all forestUNESCO has been destroyed. In this situat– ion,EOLSS afforestation appears to be the most significant option to counteract the global loss of forest. Plantation of new forests is progressing overSAMPLE an impressive total area wo rldwideCHAPTERS (sum in 2000: 187 Mha; rate ca. 4.5 Mha.a-1), with strong regional differences. Forest plantations seem to have the potential to provide suitable habitat and thus contribute to biodiversity conservation in many situations, particularly in problem areas of the tropics where strong forest loss has occurred. -
DECISION RECORD for the OREGON GULCH FIRE SALVAGE RECOVERY PROJECT (DOI-BLM-OR-M060-2015-0004-EA)
United States Department of the Interior BUREAU OF LAND MANAGEMENT MEDFORD DISTRICT OFFICE ASHLAND RESOURCE AREA 3040 Biddle Road Medford, Oregon 97504 DECISION RECORD for the OREGON GULCH FIRE SALVAGE RECOVERY PROJECT (DOI-BLM-OR-M060-2015-0004-EA) INTRODUCTION This document describes my decision, and reasons for my decision, regarding the selection of a course of action to be implemented for the Oregon Gulch Fire Salvage Recovery Project. The Medford District Bureau of Land Management (BLM), Ashland Resource Area, has completed the environmental analysis which is documented in the Oregon Gulch Fire Salvage Recovery Project Final Environmental Assessment (DOI-BLM-OR-M060-2015-0004-EA) (EA) for the proposed 683 acres of post-fire forest management recovery of BLM-administered land in the Oregon Gulch Fire area. Project activities will salvage standing dead trees, fire-injured trees, and hazard trees, rehabilitate sites through tree planting, and repair, maintain, and decommission road facilities on BLM-administered land. There will be a limited amount of temporary road construction (0.6 miles), to access salvage areas, which will be decommissioned after completion of harvest activities. The Oregon Gulch Fire Salvage Recovery Project is located on lands administered by the Medford District BLM lands in the Upper Fall Creek drainage of the Iron Gate Reservoir-Klamath River fifth field watershed and the Beaver Creek drainage of the Copco Reservoir-Klamath River fifth-field watershed. The Public Land Survey System description for the project area is: T. 40 S., R. 04 E., Sec. 25 and 35; T. 41 S., R. 04 E. in Sec. -
Project Title: Impacts of Post-Fire Salvage Logging and Wildfire Burn Intensity on Soil Productivity and Forest Recovery
Project Title: Impacts of Post-Fire Salvage Logging and Wildfire Burn Intensity on Soil Productivity and Forest Recovery JFSP Project Number: 05-2-1-44 Principal Investigator: Dr. Jane E. Smith, Research Botanist, Pacific Northwest Research Station, 3200 Jefferson Way, Corvallis, OR 97331; Phone: 541/750-7387; fax: 541/750-7329; email: [email protected] Co-Principal Investigators: Dr. David Shaw, Dept. of Forest Engineering, Resources and Management, Oregon State University, Corvallis, OR 97331, Phone: 541/737-2845; fax: 541/737-4316; email: [email protected] Dr. Elizabeth Sulzman (deceased), Dept. of Crop & Soil Science, Oregon State University, Corvallis, OR Graduate Research Assistants and Technicians: Ms. Doni McKay, Pacific Northwest Research Station, 3200 Jefferson Way, Corvallis, OR Ms. Cassie Hebel, Dept. of Forest Science, Oregon State University, Corvallis, OR Ms. Tara Jennings, Dept. of Forest Science, Oregon State University, Corvallis, OR This research was sponsored in part by the Joint Fire Science Program. For further information go to www.firescience.gov I. Abstract This project consists of two interrelated studies designed to determine how soil productivity responds to 1) post-fire salvage logging, and 2) soil burn severity in a mixed conifer forest. The project was conducted within the perimeter of the Booth and Bear Butte (B&B) Fire Complex, a large stand-replacing wildfire that burned over 36,730 hectares in the summer of 2003. In study one, we examined the effects of salvage logging operations (e.g. compaction, subsoiling) on soil productivity on 7 replicate sites, harvested 1 year after the B&B fire. Within each site, we measured the impacts of 3 treatments (burning with no further disturbance, compaction from heavy equipment, and compaction followed by subsoiling) on soil biological, chemical, and physical properties critical to soil productivity and growth of planted tree seedlings. -
Neotropical Rainforest Restoration: Comparing Passive, Plantation and Nucleation Approaches
UC Riverside UC Riverside Previously Published Works Title Neotropical rainforest restoration: comparing passive, plantation and nucleation approaches Permalink https://escholarship.org/uc/item/4hf3v06s Journal BIODIVERSITY AND CONSERVATION, 25(11) ISSN 0960-3115 Authors Bechara, Fernando C Dickens, Sara Jo Farrer, Emily C et al. Publication Date 2016-10-01 DOI 10.1007/s10531-016-1186-7 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Biodivers Conserv DOI 10.1007/s10531-016-1186-7 REVIEW PAPER Neotropical rainforest restoration: comparing passive, plantation and nucleation approaches 1,2 2 2 Fernando C. Bechara • Sara Jo Dickens • Emily C. Farrer • 2,3 2 2,4 Loralee Larios • Erica N. Spotswood • Pierre Mariotte • Katharine N. Suding2,5 Received: 17 April 2016 / Revised: 5 June 2016 / Accepted: 25 July 2016 Ó Springer Science+Business Media Dordrecht 2016 Abstract Neotropical rainforests are global biodiversity hotspots and are challenging to restore. A core part of this challenge is the very long recovery trajectory of the system: recovery of structure can take 20–190 years, species composition 60–500 years, and reestablishment of rare/endemic species thousands of years. Passive recovery may be fraught with instances of arrested succession, disclimax or emergence of novel ecosystems. In these cases, active restoration methods are essential to speed recovery and set a desired restoration trajectory. Tree plantation is the most common active approach to reestablish a high density of native tree species and facilitate understory regeneration. While this approach may speed the successional trajectory, it may not achieve, and possibly inhibit, a long-term restoration trajectory towards the high species diversity characteristic of these forests.