Forest Management to Protect Colorado's Water Resources
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Silviculture and Forest Management
Working with your forest to meet your needs: Silviculture and Forest Management Susan L. Stout US Forest Service, Northern Research Station Warren, PA Silvi • Silviculture is certainly about trees, and specifically about trees in forests …culture • The totality of socially transmitted behavior patterns, arts, beliefs, institutions, and all other products of human work and thought • www.thefreedictionary.com/culture …culture • the quality in a person or society that arises from a concern for what is regarded as excellent in arts, letters, manners, scholarly pursuits, etc dictionary.reference.com/ browse/culture Silviculture • “Silviculture is the art & science of controlling the establishment, growth, composition, health, and quality of forests & woodlands to meet the diverse needs & values of landowners & society on a sustainable basis.” Society of American Foresters 1994 Knowledge needed to practice good silviculture • Site quality and characteristics • Character of surrounding landscape • Age classes found in and around this forest stand • History of the forest • Silvics of species in the stand Site quality • Sometimes measured by the height of leading trees at a certain age, figured out by taking tree cores (if the tallest trees were removed, or the stand is uneven-aged, this may not work) • Concept integrates landscape position, many soil characteristics, dry/moist conditions, and nutrients Landscape Context Age classes of your forest Uneven-aged Even-aged Age classes of your forest Uneven-aged Even-aged • Activities planned for the -
Klamath Falls 2014 and 2015 Exceptional Event EPA Concurrence Request
Klamath Falls 2014 and 2015 Exceptional Event EPA Concurrence Request Submitted to: EPA, Region 10 By: Rachel Sakata and Anthony Barnack May 2017 Air Quality Planning 700 NE Multnomah St., Suite #600 Portland, OR 97232 Phone: (503) 229-5659 (800) 452-4011 Fax: (503) 229-6762 Contact: Rachel Sakata www.oregon.gov/DEQ DEQ is a leader in restoring, maintaining and enhancing the quality of Oregon’s air, land and water. Oregon Department of Environmental Quality This report prepared by: Oregon Department of Environmental Quality 700 NE Multnomah St., Suite #600 Portland, OR 97232 1-800-452-4011 www.oregon.gov/deq Contact: Rachel Sakata 503-229-5659 Alternative formats (Braille, large type) of this document can be made available. Contact DEQ, Portland, at 503-229-5696, or toll-free in Oregon at 1-800-452-4011, ext. 5696. State of Oregon Department of Environmental Quality ii Table of Contents Executive Summary..................................................................................................................................... 1 1. Conceptual Model ................................................................................................................................... 3 1.1 Overview .................................................................................................................................................... 3 1.2 Source Area ....................................................................................................................................................... 5 1.3 Affected Region -
Traditional Fire Knowledge in Two Chestnut Forest Ecosystems of the Iberian Peninsula and Its Implications
Land Use Policy 47 (2015) 130–144 Contents lists available at ScienceDirect Land Use Policy jo urnal homepage: www.elsevier.com/locate/landusepol Forgetting fire: Traditional fire knowledge in two chestnut forest ecosystems of the Iberian Peninsula and its implications for European fire management policy a,∗ b c a,b,c Francisco Seijo , James D.A. Millington , Robert Gray , Verónica Sanz , d e f Jorge Lozano , Francisco García-Serrano , Gabriel Sangüesa-Barreda , f Jesús Julio Camarero a Middlebury College C.V. Starr School in Spain, Madrid, Spain b Department of Geography, King’s College London, London, UK c RW Gray Consulting Ltd, Chilliwack, BC, Canada d Departamento de Ciencias Naturales, Sección de Biología Básica y Aplicada, Universidad Técnica Particular de Loja, San Cayetano Alto, C/París s/n., Loja 1101608, Ecuador e Saint Louis University, Madrid, Spain f Instituto Pirenaico de Ecologia-CSICAvda. Monta˜nana, 1005. 50059 Zaragoza, Spain a r t i c l e i n f o a b s t r a c t Article history: Human beings have used fire as an ecosystem management tool for thousands of years. In the context of Received 6 October 2014 the scientific and policy debate surrounding potential climate change adaptation and mitigation strate- Received in revised form 25 February 2015 gies, the importance of the impact of relatively recent state fire-exclusion policies on fire regimes has Accepted 14 March 2015 been debated. To provide empirical evidence to this ongoing debate we examine the impacts of state fire-exclusion policies in the chestnut forest ecosystems of two geographically neighbouring municipal- Keywords: ities in central Spain, Casillas and Rozas de Puerto Real. -
FOREST Condition Assessment Brochure, Pg
Reference TIPS FOREST Condition Assessment brochure, pg. 9 With proper management, you can maintain healthy forest land. All forests can be managed for a single use, such as timber production, or for multiple uses, such as wildlife habitat, recreation, livestock grazing and/or timber production. To help you Worksheet manage your forest land, you need to decide which of these uses are important to you. You likely have a primary use planned that will guide your overall management and decision-making processes. If secondary and tertiary uses are also important to you, allow these to guide your decisions as well. This worksheet will help you ensure that the vegetation and ecosystems on your forest land function properly for the land uses you have identified. In a healthy forest, the larger overstory trees, smaller understory trees, and ground vegetation are all in good condition. The distribution of vegetation and the number of trees per acre will differ depending upon where your property is located within the state. Soil type, precipitation, temperature, tree species, and your land use objectives are also factors that affect the density and distribution of vegetation on your forest land. Instructions: Conduct a basic assessment of your forest land by answering the following questions. Suggestions to help you address specific management issues are listed directly under each section. If you identify management needs and issues that may require professional assistance, refer to the last page of this Forest Condition Assessment for a list of resources. Site Date 1. Identify the tree species on your forest land. Select all that are present: Others: □ Douglas fi r □ Western larch □ Ponderosa pine □ Bigleaf maple □ Grand fi r □ Red alder □ White fi r □ Sitka spruce □ Western hemlock □ Oregon white oak There are many references to help you identify the tree species present in Oregon. -
Understanding the Carbon and Greenhouse Gas Balance of Forests in Britain
Research Report Understanding the carbon and greenhouse gas balance of forests in Britain Research Report Understanding the carbon and greenhouse gas balance of forests in Britain James Morison, Robert Matthews, Gemma Miller, Mike Perks, Tim Randle, Elena Vanguelova, Miriam White and Sirwan Yamulki Forestry Commission: Edinburgh © Crown Copyright 2012 You may re-use this information (not including logos) free of charge in any format or medium, under the terms of the Open Government Licence. To view this licence, visit: www.nationalarchives.gov.uk/doc/open-government-licence or write to the Information Policy Team, The National Archives, Kew, London TW9 4DU, or e-mail: [email protected]. First published in 2012 by Forestry Commission, Silvan House, 231 Corstorphine Road, Edinburgh EH12 7AT. ISBN 978-0-85538-855-3 Morison, J., Matthews, R., Miller, G., Perks, M., Randle, T., Vanguelova, E., White, M. and Yamulki, S. (2012). Understanding the carbon and greenhouse gas balance of forests in Britain. Forestry Commission Research Report. Forestry Commission, Edinburgh. i–vi + 1–149 pp. Keywords: Forest carbon; carbon stocks; soil carbon; greenhouse gas balance; mitigation; fossil fuel substitution; forest management. FCRP018/FC-GB(STUDIO9)/0K/MAR12 Enquiries relating to this publication should be addressed to: Forestry Commission 231 Corstorphine Road Edinburgh Scotland, EH12 7AT T: 0131 334 0303 E: [email protected] The Forestry Commission will consider all requests to make the content of publications available in alternative formats. Please direct requests to the Forestry Commission Diversity Team at the above address, or by email at [email protected] or by phone on 0131 314 6575. -
Natural Disturbance and Stand Development Principles for Ecological Forestry
United States Department of Agriculture Natural Disturbance and Forest Service Stand Development Principles Northern Research Station for Ecological Forestry General Technical Report NRS-19 Jerry F. Franklin Robert J. Mitchell Brian J. Palik Abstract Foresters use natural disturbances and stand development processes as models for silvicultural practices in broad conceptual ways. Incorporating an understanding of natural disturbance and stand development processes more fully into silvicultural practice is the basis for an ecological forestry approach. Such an approach must include 1) understanding the importance of biological legacies created by a tree regenerating disturbance and incorporating legacy management into harvesting prescriptions; 2) recognizing the role of stand development processes, particularly individual tree mortality, in generating structural and compositional heterogeneity in stands and implementing thinning prescriptions that enhance this heterogeneity; and 3) appreciating the role of recovery periods between disturbance events in the development of stand complexity. We label these concepts, when incorporated into a comprehensive silvicultural approach, the “three-legged stool” of ecological forestry. Our goal in this report is to review the scientific basis for the three-legged stool of ecological forestry to provide a conceptual foundation for its wide implementation. Manuscript received for publication 1 May 2007 Published by: For additional copies: USDA FOREST SERVICE USDA Forest Service 11 CAMPUS BLVD SUITE 200 Publications Distribution NEWTOWN SQUARE PA 19073-3294 359 Main Road Delaware, OH 43015-8640 November 2007 Fax: (740)368-0152 Visit our homepage at: http://www.nrs.fs.fed.us/ INTRODUCTION Foresters use natural disturbances and stand development processes as models for silvicultural practices in broad conceptual ways. -
Synthesis of Knowledge of Extreme Fire Behavior: Volume I for Fire Managers
United States Department of Agriculture Synthesis of Knowledge of Forest Service Pacific Northwest Extreme Fire Behavior: Research Station General Technical Volume I for Fire Managers Report PNW-GTR-854 November 2011 Paul A. Werth, Brian E. Potter, Craig B. Clements, Mark A. Finney, Scott L. Goodrick, Martin E. Alexander, Miguel G. Cruz, Jason A. Forthofer, and Sara S. McAllister A SUMMARY OF KNOWLEDGE FROM THE The Forest Service of the U.S. Department of Agriculture is dedicated to the principle of multiple use management of the Nation’s forest resources for sustained yields of wood, water, forage, wildlife, and recreation. Through forestry research, cooperation with the States and private forest owners, and management of the national forests and national grasslands, it strives—as directed by Congress—to provide increasingly greater service to a growing Nation. The U.S. Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, age, disability, and where applicable, sex, marital status, familial status, parental status, religion, sexual orientation, genetic information, political beliefs, reprisal, or because all or part of an individual’s income is derived from any public assistance program. (Not all prohibited bases apply to all programs.) Persons with disabilities who require alternative means for communication of program information (Braille, large print, audiotape, etc.) should contact USDA’s TARGET Center at (202) 720-2600 (voice and TDD). To file a complaint of discrimination, write USDA, Director, Office of Civil Rights, Room 1400 Independence Avenue, SW, Washington, DC 20250-9410 or call (800) 795-3272 (voice) or (202) 720-6382 (TDD). -
Attachment a ‐ Forest Service Wildfire, NEPA, and Salvage Summary
Attachment A ‐ Forest Service Wildfire, NEPA, and Salvage Summary Fiscal Year 2007 2008 2009 2010 2011 2012 2013 2014 2015 2016 2007‐2016 Number of Fires 1 63 64 53 33 66 79 56 56 127 110 707 Total fire acres on NFS 2 1,751,118 1,326,893 549,108 211,327 1,489,029 2,411,413 1,141,353 741,465 1,587,843 1,038,686 12,248,235 High severity acres on NFS 3 842,658 368,595 268,944 76,192 619,020 809,720 513,957 265,045 489,668 397,654 4,651,453 Number of NEPA decisions identified 4 129 Acres of salvage planned in NEPA 5 218 17,255 2,134 14,010 22,761 28,937 13,809 13,264 112,388 Number of NEPA decisions litigated 6 125110332422 Litigation cases won by USFS 7 013110131112 Litigation cases lost by USFS 8 1120001011 7 Litigation cases pending 9 0000001002 3 Acres of salvage reported accomplished 10 328 2,665 8,125 3,464 8,774 6,916 11,672 19,792 16,926 21,234 99,896 1 Fires burning more than 1,000 acres on NFS land 10 Salvage harvest activity records identified as awarded in Forest Service Activity 2 Total acres inside fire perimeter on NFS land Tracking System (FACTS) by GIS analysis of fire perimeters. 3 Classified as greater than 75% mortality using Rapid Assessment of Vegetation Condition after Wildfire (RAVG) 4 Identified by fire salvage keyword search in PALS (Planning Appeals and Disclaimer: Only the litigation data is believed to be 100% complete and Litigation System) or reported with sale activity records in Forest Service systems accurate. -
Forest Stand Delineation
City of Dallas Landscape and Tree Manual APPENDIX G Forest Stand Delineation Steps for Assessment Tree survey Sampling methods Tree canopy cover assessment methods Forest Stand Delineation procedures 1. Old-field succession assessment 2. Tree canopy cover credit for single-family and duplex uses 3. Tree canopy cover assessment of development impact area in conjunction with Sustainable Development Incentives (Review Appendix F) 4. Tree canopy cover assessment on properties five acres or larger with institutional and community service uses or recreation uses 5. Forest analysis for baseline documentation to create a conservation easement 6. Tree canopy cover assessment where trees are removed without authorization (10.137) The forest stand delineation is a form of site assessment prescribed for its function to evaluate for tree species size, distribution, location, and age and may be used to March 14, 2019 Appendix G: Forest Stand Delineation 1 | Page City of Dallas Landscape and Tree Manual identify tree canopy coverage for the purposes of tree mitigation calculations. A forest canopy goal is typically sought instead of mandating a forest canopy requirement. Ordinance: (22) FOREST STAND DELINEATION (“FSD”) means a comprehensive assessment of the conditions of a property using multiple types of information, including, but not limited to, a tree survey, aerial imagery collected from private or public sources, natural resources assessments, topographic maps, management plans, a map of conservation areas, land use maps, etc., to provide the required data to determine tree replacement requirements and forest conservation objectives. (B) A forest stand delineation (“FSD”) used for the purpose of calculating the total square footage of forest canopy coverage of building sites and providing an ecological assessment of a property. -
August 13, 2018 Northwest Zone Interagency Fire Coordination Group
Northwest Zone Interagency Fire Coordination Group Jump to: Evacuations | Fire Weather | Fire Restriction Discussion | Fire Updates | Air Quality | Prevention Message | Media Contacts RELEASE DATE: Monday, August 13, 2018 – 15:30 p.m. Current Fire Danger: EXTREME FIRE RESTRICTIONS: All jurisdictional agencies in the NW Zone Fire Management Area will enter Stage II Restrictions at 12:01 a.m. Thursday, August 16, 2018. This includes: Flathead National Forest, Flathead County, DNRC NW Land Office Kalispell, Libby, Plains Units; Kootenai National Forest, Lincoln County, Sanders County, Lake County. Glacier National Park is entering Stage II Fire Restrictions at 12:01 a.m. Tuesday, August 14. Current Restrictions: Sanders County: Stage II Kootenai National Forest: Stage I Libby & Plains Units, Montana DNRC: Stage I MULTIPLE LIGHTNING STRIKES ACROSS THE FIRE AREA WERE RECORDED SATURDAY, AUGUST 11, 2018, WITH CONFIRMED FIRES IN ALL JURISDICTIONS. MULTIPLE FIRE REPORTS ARE COMING IN, WITH INITIAL ATTACK OCCURING, RESOURCES RESPONDING, AND MORE FIREFIGHTING RESOURCES BEING ORDERED. A SIZE-UP OF THE BIG PICTURE ACROSS THE AREA IS OCCURING NOW, AND PRIORITIES BEING DETERMINED. Evacuations Glacier National Park 9 p.m. 8/12/2018: Howe Ridge Fire Evacuation Order: Avalanche and Sprague Creek Campgrounds, North Lake McDonald Road (including private residences and Lake McDonald Ranger Station), Lake McDonald Lodge Complex (all businesses, employees, and private residences), private residences along Going-to-the-Sun Road. The Going-to-the-Sun Road is closed near Apgar to Logan Pass on the west side. Apgar Village and most other areas of the park remain open. Glacier National Park Fire Line: 406-888-7077 U.S. -
Lake Fire June/July 2015
Lake Fire June/July 2015 Page 1 USDA-FOREST SERVICE FS-2500-8 (6/06) Date of Report: July 8, 2015 BURNED-AREA REPORT (Reference FSH 2509.13) PART I - TYPE OF REQUEST A. Type of Report [x] 1. Funding request for estimated emergency stabilization funds [ ] 2. Accomplishment Report [ ] 3. No Treatment Recommendation B. Type of Action [x] 1. Initial Request (Best estimate of funds needed to complete eligible stabilization measures) [ ] 2. Interim Report #____ [ ] Updating the initial funding request based on more accurate site data or design analysis [ ] Status of accomplishments to date [ ] 3. Final Report (Following completion of work) PART II - BURNED-AREA DESCRIPTION A. Fire Name: Lake B. Fire Number: CA-BDF- 7894 C. State: CA D. County: San Bernardino E. Region: 05 F. Forest: San Bernardino G. District: Front Country/Mountaintop H. Fire Incident Job Code: P5JS38 I. Date Fire Started: June 17, 2015 J. Date Fire Contained: N/A K. Suppression Cost: Est. $34,000,000 L. Fire Suppression Damages Repaired with Suppression Funds 1. Fireline waterbarred (miles):56.2 2. Fireline seeded (miles): 3. Other (identify): M. Watershed Number: 180702030201 Fish Creek-Santa Ana River, 180702030202 Deer Creek-Santa Ana River, 180702030501 Mill Creek, 181001000601 Rattlesnake Spring-Rattlesnake Canyon, 181001000901 Pipes Spring-Pipes Wash, 181001000902 Antelope Creek, 181002010301 South Fork Whitewater River- Whitewater River, 181002010303 Mission Creek, 181002010402 Little Morongo Creek, and 181002010401 Big Morongo Creek N. Total Acres Burned: NFS Acres (23,387) Other Federal (1,861) State (0) Private (5,240) O. Vegetation Types: Upper montane conifer forest , subalpine conifer forest, montane chaparral, meadow, riparian, pinyon/juniper, joshua tree, great basin sage, and desert transitional chaparral. -
Growth and Yield in Uneven-Aged Stands
We can perhaps think of two main categories of growth and yield estimates: (1) estimates of current growth of existing stands, with projections for short periods into the future assuming continuation of current management practices; and (2) estimates of growth and yield under long term applica tion of possible management regimes, intended in part at least to identify options and provide a basis for choice among alternatives. The first usually comes from inventories of existing conditions. The second, from construction of some type of predictive model, often based on quite limited data from small experimental areas, since the stand conditions concerned may not as yet exist over the forest as a whole. Here, I am talking pri · marily about this second type of estimate. Basic Differences Between Even-aged and Uneven-aged Stands 1. Areal arrangement by age classes: By definition, an even-aged stand is composed of one main age class over an area large enough to be mappable and recognized as a distinct unit in management. An uneven-aged stand is anything else, and consists of two to many age classes in any areal arrangement from stemwise mixture to even aged groups of up to several acres each. 2. Diameter distributions: The- even-aged stand has the typical bell-shaped diameter distribution, while the uneven-aged stand--considered over any substantial area--has a more or less J-shaped distribution (which may be a summation of other distributions for numerous small areas) . 3. Height growth: Even-aged stands: Dominants have a well-defined and consistent sigmoid growth pattern characteristic of the site.