Forest Practice Guidelines for Tennessee
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Sustainable Forestry
FNR-182 Purdue University - Forestry and Natural Resources & Natural Re ry sou st rc re e o s F A Landowner’s Guide to Sustainable Forestry in Indiana PURDUE UNIVERSITY Part 3. Keeping the Forest Healthy and Productive Ron Rathfon, Department of Forestry and Natural Resources, Purdue University Lenny Farlee, Indiana Department of Natural Resources, Division of Forestry Sustainable forest Environmental Factors Affecting management requires an Forest Growth and Development understanding of site productivity and heredi- • Climate tary factors that affect • Soil forest growth and devel- • Topography or lay of the land opment, as well as factors • Fungi, plant & animal interactions like climate, soil, topogra- phy or lay of the land, and • Disturbances how fungi, plants, and animals interact and help A remarkable variety of forests grow in Indiana. Over or harm each other. 100 different native species of trees intermingle in Ron Rathfon Sustainable forest various combinations. They flourish in swamps, anchor Deep soils and ample soil management also requires sand dunes, cling precariously to limestone precipices, moisture on this northeast- knowledge of each bind riverbanks against ravaging spring floods, and sink facing, upland site promote species’ unique needs and tap roots deep into rich, fertile loam. the growth of a lush adaptations, how a forest understory shrub layer and Trees, like all other green plants, require sunlight, heat, changes over time, and fast-growing, well-formed how it responds when water, nutrients, and space to thrive. Environment trees. determines the availability of essential requirements. disturbed by fire, insect Foresters refer to this availability as site productivity. outbreak, tornado, or timber harvesting. -
High Grade Harvesting It Is Important to Note That There Is a Wide Range of Variability to High Grading
HighGrade Harvesting Understand the impacts, know your options. Paul Catanzaro University of Massachusetts Amherst Anthony D'Amato University of Massachusetts Amherst Introduction “ I thought I did the As a landowner, you may be approached by a logger or forester to have a “high grade” harvest of your RIGHT THING. woods, which they typically call “selective cutting.” Selective cutting refers to a harvest that does not I did a selective cut all of the trees. cut, not a clearcut. However, there are many forms of selective cutting. While high grading does leave trees after the I WAS TOLD harvest, the critical issues to consider are whether the harvest will meet your immediate goals and if the that I could be remaining trees will best meet your future goals. back in there All woodlands do not provide equal benefits. The number, size, type, and quality of the trees left after cutting IN harvesting all affect what your woods will become in the future and, as a direct result, what benefits your woods 10 YEARS.” will provide to you and those that follow. High grading generally takes the best trees and leaves the rest, and may not meet your needs. This pamphlet will help you make informed decisions about the sale of timber from your land by providing information on high grading and forest management using silviculture. It also gives you information on resources and professional foresters who can help you. 3 Definitions High Grading SILVICULTURE High grading liquidates the value of the woods by: Silviculture - The art and science of controlling the ❶ Removing the largest, most valuable trees and, establishment, growth, composition, health, and quality of forests to meet the diverse needs and ❷ Increasing the composition of the poorer quality and values of landowners and society on a sustainable traditionally low-value species (e.g., red maple, beech, basis. -
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%). -
BEL Deforestation Solution
BEL Deforestation Solution I. Abstract Deforestation is the result of forests decreasing due to people illegally cutting down trees and wild fires. It increases CO2 in the atmosphere, which leads to global warming. It is destroying the habitats of many animals and beautiful forests. According to the World Wildlife Organization, 15% of all greenhouse gas emissions are caused by deforestation. Additionally, the World Wildlife Organization says that 1.25 billion people worldwide rely on forests for shelter, livelihood, water, fuel, and food security. Our future technology solution is artificial trees to power the drones and absorb CO2 as well as drones to protect our forest, put out fires, and replant trees. II. Description 1. Present Technology Satellite monitoring is currently used to understand if the forests are changing and what are the causes for those changes. One example of this is Global Forest Watch 2.0. It was developed by “Google, in partnership with the University of Maryland and the UN Environment Programme,” according to enviromentalleader.com. This forest watch uses “satellite technology, data sharing and human networks around the world.”1 The purpose of this is to give real-time information regarding deforestation to all countries across the world. The limitation is it’s a monitoring system, and cannot actually stop deforestation without something to act on it. One current technology that exists for replanting trees is drone planting. Drone planting is drones dropping seed pods. Over time, the pods dissolve and the seeds pop out. The benefits of this technology are that this can easily reach hard-to find areas. -
The Ecological Roots of New Approaches to Forestry by Fred Swanson and Dean Berg
The Ecological Roots of New Approaches to Forestry by Fred Swanson and Dean Berg uring the 1940s through the cepts of natural disturbance and suc- played a pivotal role in this transfor- 1980s, forest management cessional processes. Itwas commonly mation. In the broadest sense, we are and research in the Pacific argued, for example, that clearcutting moving from treating forest manage- Northwest focused largely mimics natural disturbance by wild- ment as a series of discreet operations on harvesting natural stands fire-but is not as wasteful because to viewing forests as ecological sys- and establishing Douglas fir the wood is harvested and used. tems. One of the central components plantations. This was accomplished But, forestry is in the midst of a ofthis emerging emphasis on integra- with relative efficiency by clearcutting, major transformation. A5HalSalwasser tive management is leaving residual burning woody residues, establishing of the u.s. Forest Service New Per- forest structures (e.g., trees, snags, dense stands of a single tree species, spectives Program has pointed out, down logs,) as biological legacies to hastening crown closure, suppressing we are involved in an evolution across be carried over from one stand to the competing vegetation, and other prac- three stages of natural resource man- next. tices. From an economic perspective, agement: from regulation of uses, to Although some of the techniques such intensive silvicultural practices sustained yield management, to sus- involved in managing biologicallega- provided a relatively high short-term tainable ecosystem management. Re- cies may be relatively new, the under- return on investment. Biologically, search within and at the interfaces lyingconcepts have evolved over more these practices seemed at least super- between wildlife biology, fisheries, than a decade. -
FIGHTING FIRE with FIRE: Can Fire Positively Impact an Ecosystem?
FIGHTING FIRE WITH FIRE: Can Fire Positively Impact an Ecosystem? Subject Area: Science – Biology, Environmental Science, Fire Ecology Grade Levels: 6th-8th Time: This lesson can be completed in two 45-minute sessions. Essential Questions: • What role does fire play in maintaining healthy ecosystems? • How does fire impact the surrounding community? • Is there a need to prescribe fire? • How have plants and animals adapted to fire? • What factors must fire managers consider prior to planning and conducting controlled burns? Overview: In this lesson, students distinguish between a wildfire and a controlled burn, also known as a prescribed fire. They explore multiple controlled burn scenarios. They explain the positive impacts of fire on ecosystems (e.g., reduce hazardous fuels, dispose of logging debris, prepare sites for seeding/planting, improve wildlife habitat, manage competing vegetation, control insects and disease, improve forage for grazing, enhance appearance, improve access, perpetuate fire- dependent species) and compare and contrast how organisms in different ecosystems have adapted to fire. Themes: Controlled burns can improve the Controlled burns help keep capacity of natural areas to absorb people and property safe while and filter water in places where fire supporting the plants and animals has played a role in shaping that that have adapted to this natural ecosystem. part of their ecosystems. 1 | Lesson Plan – Fighting Fire with Fire Introduction: Wildfires often occur naturally when lightning strikes a forest and starts a fire in a forest or grassland. Humans also often accidentally set them. In contrast, controlled burns, also known as prescribed fires, are set by land managers and conservationists to mimic some of the effects of these natural fires. -
News from the Virginia Tree Farm Foundation By: John Matel, Virginia Tree Farm Foundation
News from the Virginia Tree Farm Foundation By: John Matel, Virginia Tree Farm Foundation New certification fees I have been a certified Tree Farmer since I bought my first forest land in 2005. Being a certified Tree Farmer is important to me. In fact, it is so important that I have served as the President of the Virginia Tree Farm Foundation (VTFF) for the past 4 years. Until now, this program has been free in Virginia, even as many other states instituted various fees. However, now Virginia will be following suit. Starting January 1, current Virginia Tree Farmers will be billed a certification fee of $50 per year per Tree Farm. The VTFF recognizes that some people own multiple Tree Farms so there is a maximum fee. No Tree Farmer will pay more than $250 per year, no matter how many individual Tree Farms they own. New Tree Farms will be assessed a one-time certification fee of $100, which will cover initial costs plus their first year of Tree Farm certification. These fees will be used to cover administrative expenses associated with the VTFF, offer better service to Tree Farmers, and allow for more outreach and educational opportunities. Something new: Landscape Management Plans Virginia has been chosen to pilot a Landscape Management Plan (LMP). The LMP will cover all counties east of, and those including, Route 29. The LMP will allow for more planning at the landscape, rather than at the individual property, scale. Tree Farmers may opt to have their own management plan; however, they will also have the option of using the LMP. -
Prescribed Fire 101 Controlling Fire for Ecological Benefits
Prescribed Fire 101 Controlling Fire for Ecological Benefits The very foundation of fire ecology is the premise that wildland fire is neither innately destructive nor in the best interest of every forest. Fire causes change and change has its own value. Certain forest biomes benefit more than others. Change by fire is biologically necessary to maintain many healthy ecosystems in fire-loving plant communities and resource managers have learned to use fire to cause changes in plant and animal communities to meet their objectives. Varying fire timing, frequency, and intensity produces differing resource responses that create the correct changes for habitat manipulation. A History of Fire Indigenous peoples used fire in virgin pine stands to provide better access, improve hunting, and ridding the land of undesirable species so they could farm. Early settlers observed this and many continued the practice of using fire as a beneficial agent. Destructive wildfire was also prevented by burning under safer conditions with the necessary tools for control. An appropriately "controlled" burn would reduce fuels that fed dangerous fires and assure that the next fire season would not bring destructive, property damaging fire. But increased tree planting and an encroaching urban interface called attention the wildfire problem and led foresters to advocate the exclusion of all fire from the woods. This, in part, was due to the wood boom after WWII and the planting of millions of acres of susceptible trees that were vulnerable to fire in the first few years of establishment. This "exclusion of fire" was not always an acceptable option - and this dramatically learned in Yellowstone National Park after decades of excluding fire. -
Patterns of Plant Community Structure Within and Among Primary and Second-Growth Northern Hardwood Forest Stands
Forest Ecology and Management 258 (2009) 2556–2568 Contents lists available at ScienceDirect Forest Ecology and Management journal homepage: www.elsevier.com/locate/foreco Patterns of plant community structure within and among primary and second-growth northern hardwood forest stands Julia I. Burton a,*, Eric K. Zenner b, Lee E. Frelich c, Meredith W. Cornett d a Department of Forest and Wildlife Ecology, University of Wisconsin – Madison, 1630 Linden Drive, Madison, WI 53706, United States b School of Forest Resources, The Pennsylvania State University, 305 Forest Resources Building, University Park, PA 16802, United States c Department of Forest Resources, University of Minnesota, 115 Green Hall, 1530 Cleveland Avenue North, St. Paul, MN 55108, United States d The Nature Conservancy in Minnesota, 394 Lake Avenue South, Duluth, MN 55802, United States ARTICLE INFO ABSTRACT Article history: Forest scientists advocate the use of natural disturbance-based forest management for restoring the Received 4 May 2009 characteristics of old-growth forests to younger second-growth northern hardwood stands. However, Received in revised form 4 August 2009 prescriptions rely upon studies that have (1) not spanned the full range of conditions and species Accepted 5 September 2009 assemblages, and (2) focused primarily on contrasting old-growth and mature second-growth stands at a single scale. To examine how the legacy of historical logging activities influences forest structure and Keywords: function, we compared and contrasted patterns of plant community structure within and among second- Forest structure growth and primary stands on the north shore of Lake Superior in Minnesota, USA — near the current Natural disturbance-based forest range limits of the dominant species, sugar maple (Acer saccharum). -
2.4 Effects of Controlled Burns on the Bulk Density and Thermal Conductivity of Soils at a Southern Colorado Site W. J. Massman1
2.4 Effects of controlled burns on the bulk density MEF is a forested, high elevation, semi-arid, site and thermal conductivity of soils at a dominated by ponderosa pine (Pinus ponderosa) and southern Colorado site by soils that are derived mostly from biotite gran- ite and associated igneous rocks of the Pikes Peak W. J. Massman1,2 and J. M. Frank2 batholith. Two different MEF experimental burn sites were used for this study. The first site, burned in January 2002, is described by Massman et al. (2003) 1. Introduction and Massman and Frank (2004). The second site, de- Throughout the world fire plays an important role scribed by Massman et al. (2006), was burned during in the management and maintenance of ecosystems. April of 2004. Both these sites have moderately dis- However, if a fire is sufficiently intense, soil can be turbed soils, but the first burn site had once been used irreversibly altered and the ability of vegetation, par- as an access road to other parts of the forest, so the ticularly forests, to recover after a fire can be seriously soils there are more compacted (hence denser) than at compromised. Because fire is frequently used by land the second site. The consequences of this additional managers to reduce surface fuels, it is important to complication to the sampling strategy at the first site know if and how soil properties may change as a con- are discussed in more detail below. sequence of the fire-associated soil heat pulse. At the time we sampled the soils more than 3.5 years The present study outlines an experiment to deter- had passed after the first burn and about 1.5 years mine the effect that controlled burns can have on the had elapsed after the second. -
FSA1091 Basics of Heating with Firewood
DIVISION OF AGRICULTURE RESEARCH & EXTENSION Agriculture and Natural Resources University of Arkansas System FSA1091 Basics of Heating with Firewood Sammy Sadaka Introduction Many options of secure, wood combustion Ph.D., P.E. stoves, freplaces, furnaces and boilers Associate Professor Wood heating was the predominant are available in the market. EPA certifed freplaces, furnaces and wood stoves with Extension Engineer means for heating in homes and businesses for several decades until the advent of no visible smoke and 90 percent less iron radiators, forced air furnaces and pollution are among alternatives. Addi- John W. Magugu, Ph.D. improved stoves. More recently, a census tionally, wood fuel users should adhere Professional Assistant by Energy Information Administration, to sustainable wood management and EIA, has placed fuelwood users in the environmental sustainability frameworks. USA at 2.5 million as of 2012. Burning wood has been more common Despite the widespread use of cen- among rural families compared to families tral heating systems, many Arkansans within urban jurisdictions. Burning wood still have freplaces in their homes, with has been further incentivized by more many others actively using wood heating extended utility (power) outages caused systems. A considerable number of by wind, ice and snowstorms. Furthermore, Arkansans tend to depend on wood fuel liquefed petroleum gas, their alternative as a primary source of heating due to fuel, has seen price increases over recent high-energy costs, the existence of high- years. effciency heating apparatuses and Numerous consumers continue to have extended power outages in rural areas. questions related to the use of frewood. An Apart from the usual open freplaces, important question is what type of wood more effcient wood stoves, freplace can be burned for frewood? How to store inserts and furnaces have emerged. -
Tennessee Christmas Tree Production Manual
PB 1854 Tennessee Christmas Tree Production Manual 1 Tennessee Christmas Tree Production Manual Contributing Authors Alan B. Galloway Area Farm Management Specialist [email protected] Megan Bruch Leffew Marketing Specialist [email protected] Dr. David Mercker Extension Forestry Specialist [email protected] Foreword The authors are indebted to the author of the original Production of Christmas Trees in Tennessee (Bulletin 641, 1984) manual by Dr. Eyvind Thor. His efforts in promoting and educating growers about Christmas tree production in Tennessee led to the success of many farms and helped the industry expand. This publication builds on the base of information from the original manual. The authors appreciate the encouragement, input and guidance from the members of the Tennessee Christmas Tree Growers Association with a special thank you to Joe Steiner who provided his farm schedule as a guide for Chapter 6. The development and printing of this manual were made possible in part by a USDA specialty crop block grant administered through the Tennessee Department of Agriculture. The authors thank the peer review team of Dr. Margarita Velandia, Dr. Wayne Clatterbuck and Kevin Ferguson for their keen eyes and great suggestions. While this manual is directed more toward new or potential choose-and-cut growers, it should provide useful information for growers of all experience levels and farm sizes. Parts of the information presented will become outdated. It is recommended that prospective growers seek additional information from their local University of Tennessee Extension office and from other Christmas tree growers. 2 Tennessee Christmas Tree Production Manual Contents Chapter 1: Beginning the Planning ...............................................................................................