Proceedings of the Conference on Diameter-Limit Cutting in Northeastern Forests
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
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. -
Environmental Effects of Stump and Root Harvesting
Research Note Environmental effects of stump and root harvesting Andy Moffat, Tom Nisbet and Bruce Nicoll September 2011 The removal of tree stumps and coarse roots from felling sites as a source of woody biomass for bioenergy generation is well established in parts of Europe, and interest has been expressed in replicating this practice in some regions of the UK. Overseas research shows that stump harvesting can pose a risk to sustainable forest management, unless care is taken in site selection and operational practice. Poor practice can lead to detrimental effects on soil structure, increasing the risk of soil erosion, and depletes soil nutrient and carbon capital. Stump and root harvesting can also have impacts on woodland biodiversity, archaeological heritage and tree health. This Research Note offers a synthesis of available evidence on the effects of stump harvesting, drawn from largely overseas sources but critically considered for their applicability to British conditions. The overall environmental effects of stump harvesting on forest sites in the UK, and the relative magnitude of these effects compared with conventional restock site preparation, are under ongoing investigation. The results will be used to develop more definitive guidance. Preliminary guidance published by Forest Research sets out how the risks of potential damaging effects can be minimised, notably by careful assessment of site suitability and location of activities on low risk sites. It is recommended that this is used to guide the planning and location of stump and root harvesting operations in Britain. FCRN009 1 Introduction Figure 1 A tracked excavator (a) fitted with a stump removal head (b). -
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. -
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). -
Tree and Stump Removal Policy (PDF)
City of Green Bay Parks, Recreation, and Forestry Department Policies and Procedures General Subject: Forestry Specific Subject: Tree and Stump Removal Authorization/Date: November 28, 2006 Park Committee December 5, 2006 Common Council Legal References: Municipal Code Chapter 25 State Statute 27.09 Policy Statement The City shall have the authority and jurisdiction to remove trees within the rights-of-way of all streets, alleys, avenues, lanes, and public properties and parks and tree-planting easements as may be necessary to insure public safety or to preserve or enhance the symmetry and beauty of such public property. (Municipal Code Chapter 25) Trees historically maintained by the City fall under this policy. I. Definitions A. Chronic Pathogen – a disease, virus, or bacteria that will eventually cause the death of the tree B. Crown Area – the air space that a full, healthy tree crown would occupy (varies by species) C. Decay Pathogen – a fungus or canker rot that will compromise the strength and/or structure of the wood in the tree to the point that the tree becomes a hazard D. Forester – the City Forester, Assistant City Forester, or Department of Parks, Recreation and Forestry designee E. Infectious Pathogen – a disease, virus, bacteria, or fungus - that has the ability to pass from tree to tree through grafting, insect vector, or other method - that will eventually cause the death of the infected tree F. Invasive Species – trees, plants, and insects recognized by the Wisconsin DNR as detrimental to the environment of Wisconsin G. Mortality Causing Insect – invasive species insects known to kill trees if left uncontrolled H. -
Stump Removal:Removal: Selectedselected Bibliographybibliography by Dr
StumpStump Removal:Removal: SelectedSelected BibliographyBibliography by Dr. Kim D. Coder School of Forest Resources University of Georgia June 2003 This publication was prepared to assist professionals interested in exploring all aspects of stump removal to enter the literature. This bibliography is not comprehensive, but was designed to highlight important works and authors. Many of these papers have literature citations which lead to many other sources on various aspects of stump removal and decay. Anderson, C.J., M.P. Coutts, R.M. Ritchie, & D.J. Campbell. 1989. Root extraction force measurements for sitka spruce. Forestry 62(2):127-137. Biller, C.J. & J.E. Baumgras. 1987. Failure loads of small diameter hardwood stumps. Transactions of the ASAE 30(6):1587-1590. Coder, K.D. 2003. Accelerating stump decay processes. University of Georgia School of Forest Resources publication FOR03-13. Pp.7. Coder, K.D. 2003. Removing tree stumps from landscapes. University of Georgia School of Forest Resources publication FOR03-11. Pp.6. Coder, K.D. 2003. Stump removal by accelerated decay: Field worksheet. University of Georgia School of Forest Resources publication FOR03-15. Pp.2. Coder, K.D. 2003. Stump removal methods. University of Georgia School of Forest Resources publication FOR03-12. Pp.7. Coutts, M.P. 1983. Root architecture and tree stability. Plant and Soil 71:171-188. Deans, J.D. & E.D. Ford. 1983. Modeling root structure and stability. Plant and Soil 71:189-195. Entry, J.A. & C.B. Backman. 1995. Influence of carbon and nitrogen on cellulose and lignin degradation in forest soils. Canadian Journal of Forest Research 25(8):1231-1236. -
2021 National 4-H Forestry Invitational Glossary
2021 National 4-H Forestry Invitational Glossary http://www.4hforestryinvitational.org/ N4HFI Information The National 4-H Forestry Invitational is the national championship of 4-H forestry. Each year, since 1980, teams of 4-H foresters have come to Jackson's Mill State 4-H Conference Center at Weston, WV, to meet, compete, and have fun. Jackson's Mill State 4-H Conference Center is the first and oldest 4-H camp in the United States and is operated by West Virginia University Extension. NATIONAL 4-H FORESTRY INVITATIONAL GLOSSARY CONTENTS Page Trees ................................................................................................ 1 Forests & Forest Ecology ................................................................... 6 Forest Industry ............................................................................... 10 Forest Measurements & Harvesting ................................................. 11 Tree Health (Insects, Diseases, and Other Stresses) ....................... 16 Topography & Maps ........................................................................ 17 Compass & Pacing ........................................................................... 18 Second Edition, February 2019 Original Editors, Todd Dailey, Chief Appraiser and 4-H Volunteer Leader, Farm Credit of Florida; David Jackson, Forestry Educator, Penn State Extension; Daniel L. Frank, Entomology Extension Specialist & Assistant Professor, West Virginia University; David Apsley, Natural Resources Specialist, Ohio State University Extension; -
The Hidden Disaster of New York's Forest Economy
Selective Logging The Hidden Disaster of New York’s Forest Economy What Woodland Owners Should Know Definitions Silviculture The art and science of controlling the establishment, growth, composition, and health of forests and woodlands to meet the diverse needs of landowners and society on a sustainable basis. Silviculture is the unique science and technique, or tool that forestry offers in service to people. Sustainable Forest Management The practice of meeting the forest resource needs and values of the present without compromising the similar capability of future generations. High-grading A timber harvest that removes the trees of commercial value, leaving small trees, as well as large ones of poor quality and of low-value species in the forest. Selective Logging Any timber harvest that leaves a substantial number of trees. The term can refer to harvests that meet good silvicultural standards. It is more often used to describe high-grading where all of the most valuable trees are selectively cut – usually leaving a woodlot filled with poor quality trees and trees of non-commercial species. Before High-grading After High-grading Selective logging in the form of high-grading is hard to recognize from a distance, yet it can significantly reduce timber productivity. The poor quality of New York’s timber resource is a direct consequence of past high-grading. Forest owners, loggers, and mills are losing hundreds of millions of dollars in unrealized potential future income. This is why selective logging is the hidden disaster of the forest economy. The Hidden Disaster of Selective Logging Most forest land in New York State is owned by families and individuals. -
Growth Performance of Teak ( Tectona Grandis Linn
CHOWDHURY, RASHID & AFRAD 245 Tropical Ecology 49 (2): 245-250, 2008 ISSN 0564-3295 © International Society for Tropical Ecology www.tropecol.com Growth performance of Teak ( Tectona grandis Linn. f.) coppice under different regimes of canopy opening MD. QUMRUZZAMAN CHOWDHURY 1* , A.Z.M. MANZOOR RASHID 1 & MD. MASUDUZZAMAN AFRAD 2 1Department of Forestry and Environmental Sciences, Shahjalal University of Science and Technology, Sylhet-3114, Bangladesh 2Bangladesh Forest Department, Bhan Bhaban, Dhaka-1212, Bangladesh Abstract: Growth performance of Tectona grandis coppice was investigated under different canopy openings which is an important reforestation tool. Removal of single tree was done for small canopy opening; two trees for medium, and clear felling for large canopy opening. It was observed that, canopy opening did not affect survival rate and number of sprouts. However, stump height affected the number of sprouts; the maximum number of sprouts was found in 10-20 cm stump height from the ground level. In addition, number of sprouts was correlated (p<0.05) with tree and stump diameter. Both diameter and height of sprouts did not differ significantly in the earlier stage (in 6 months) with the space available due to canopy opening, whereas diameter and height growth of sprouts significantly varied when sprouts were getting old (1 year old and onward). Results indicated the potential of coppice management to restore the gaps in the prevailing plantations. Resumen: El desempeño en el crecimiento de un bosquecillo formado por rebrote de Tectona grandis fue investigado bajo diferentes aperturas del dosel, las cuales son una herramienta importante de reforestación. Para una abertura pequeña se removió un solo árbol; se removieron dos árboles para una abertura mediana, y se realizó un aclareo total del rodal para la abertura grande del dosel. -
Forest Operations Manual
INTRODUCTION Timber sales have been performed on State forest and park lands for 88 years since 1911 when the first thinning operation was completed on the Monadnock Reservation in Jaffrey. This first project coincided with the hiring of the first New Hampshire State Forester and the establishment of the State Forestry Department in 1910. During early times, timber cutting was irregularly scheduled and was primarily related to forest and park improvements as State land was acquired. Major accomplishments included the extensive thinnings, plantings, and other forest improvements performed by the Federal Civilian Conservation Corps from 1933 to 1941, and the salvage between 1939 and 1943 of huge volumes of timber damaged during the 1938 hurricane. Since 1950, however, timber sales have been regularly scheduled and have become fundamental to the management and maintenance of the timber, wildlife, and other forest resources on State-owned forest lands. Today, there are approximately a dozen or more timber sales initiated each year on State-owned lands. A typical timber sale involves an exhaustive 46 steps from start to finish, averages over 215,000 board feet, lasts six weeks (once operational), and requires more than 155 man-hours of staff time to complete. Significantly, the most demanding and time consuming portion of each timber sale is the environmental and site analysis, planning, project approval, and layout activities which generally involve almost 70 percent of the total time required for each timber sale. The key to successful timber sales on State-owned forest lands is the availability of State, Federal, and private resource management specialists to assistance with the extensive planning and review for each project. -
Simple Taper: Taper Equations for the Field Forester
SIMPLE TAPER: TAPER EQUATIONS FOR THE FIELD FORESTER David R. Larsen1 Abstract.—“Simple taper” is set of linear equations that are based on stem taper rates; the intent is to provide taper equation functionality to field foresters. The equation parameters are two taper rates based on differences in diameter outside bark at two points on a tree. The simple taper equations are statistically equivalent to more complex equations. The linear equations in simple taper were developed with data from 11,610 stem analysis trees of 34 species from across the southern United States. A Visual Basic program (Microsoft®) is also provided in the appendix. INTRODUCTION Taper equations are used to predict the diameter of a tree stem at any height of interest. These can be useful for predicting unmeasured stem diameters, for making volume estimates with variable merchantability limits (stump height, minimum top diameter, log lengths, etc.), and for creating log size tables from sampled tree measurements. Forest biometricians know the value of these equations in forest management; however, as currently formulated, taper equations appear to be very complex. Although standard taper equations are flexible and produce appropriate estimates, they can be difficult for many foresters to calibrate or use. Most foresters would not use taper equations unless they are embedded within a computer program. Additionally, very few would consider collecting the data to parameterize the equations for their local conditions. The typical taper equation formulations used today are a splined set of two or three polynomials that are usually quadratic (2nd-order polynomial) or cubic (3rd-order polynomial) (Max and Burkhart 1976).