Forest Trees of Maine
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Western Juniper Woodlands of the Pacific Northwest
Western Juniper Woodlands (of the Pacific Northwest) Science Assessment October 6, 1994 Lee E. Eddleman Professor, Rangeland Resources Oregon State University Corvallis, Oregon Patricia M. Miller Assistant Professor Courtesy Rangeland Resources Oregon State University Corvallis, Oregon Richard F. Miller Professor, Rangeland Resources Eastern Oregon Agricultural Research Center Burns, Oregon Patricia L. Dysart Graduate Research Assistant Rangeland Resources Oregon State University Corvallis, Oregon TABLE OF CONTENTS Page EXECUTIVE SUMMARY ........................................... i WESTERN JUNIPER (Juniperus occidentalis Hook. ssp. occidentalis) WOODLANDS. ................................................. 1 Introduction ................................................ 1 Current Status.............................................. 2 Distribution of Western Juniper............................ 2 Holocene Changes in Western Juniper Woodlands ................. 4 Introduction ........................................... 4 Prehistoric Expansion of Juniper .......................... 4 Historic Expansion of Juniper ............................. 6 Conclusions .......................................... 9 Biology of Western Juniper.................................... 11 Physiological Ecology of Western Juniper and Associated Species ...................................... 17 Introduction ........................................... 17 Western Juniper — Patterns in Biomass Allocation............ 17 Western Juniper — Allocation Patterns of Carbon and -
Western Juniper Field Guide: Asking the Right Questions to Select Appropriate Management Actions
Western Juniper Field Guide: Asking the Right Questions to Select Appropriate Management Actions Circular 1321 U.S. Department of the Interior U.S. Geological Survey Cover: Photograph taken by Richard F. Miller. Western Juniper Field Guide: Asking the Right Questions to Select Appropriate Management Actions By R.F. Miller, Oregon State University, J.D. Bates, T.J. Svejcar, F.B. Pierson, U.S. Department of Agriculture, and L.E. Eddleman, Oregon State University This is contribution number 01 of the Sagebrush Steppe Treatment Evaluation Project (SageSTEP), supported by funds from the U.S. Joint Fire Science Program. Partial support for this guide was provided by U.S. Geological Survey Forest and Rangeland Ecosystem Science Center. Circular 1321 U.S. Department of the Interior U.S. Geological Survey U.S. Department of the Interior DIRK KEMPTHORNE, Secretary U.S. Geological Survey Mark D. Myers, Director U.S. Geological Survey, Reston, Virginia: 2007 For product and ordering information: World Wide Web: http://www.usgs.gov/pubprod Telephone: 1-888-ASK-USGS For more information on the USGS--the Federal source for science about the Earth, its natural and living resources, natural hazards, and the environment: World Wide Web: http://www.usgs.gov Telephone: 1-888-ASK-USGS Any use of trade, product, or firm names is for descriptive purposes only and does not imply endorsement by the U.S. Government. Although this report is in the public domain, permission must be secured from the individual copyright owners to reproduce any copyrighted materials con- tained within this report. Suggested citation: Miller, R.F., Bates, J.D., Svejcar, T.J., Pierson, F.B., and Eddleman, L.E., 2007, Western Juniper Field Guide: Asking the Right Questions to Select Appropriate Management Actions: U.S. -
Hemlock Woolly Adelgid Fact Sheet
w Department of HEMLOCK WOOLLY ADELGID RK 4 ATE Environmental Adelges tsugae Conservation ▐ What is the hemlock woolly adelgid? The hemlock woolly adelgid, or HWA, is an invasive, aphid-like insect that attacks North American hemlocks. HWA are very small (1.5 mm) and often hard to see, but they can be easily identified by the white woolly masses they form on the underside of branches at the base of the needles. These masses or ovisacs can contain up to 200 eggs and remain present throughout the year. ▐ Where is HWA located? HWA was first discovered in New York State in 1985 in the lower White woolly ovisacs on an Hudson Valley and on Long Island. Since then, it has spread north to eastern hemlock branch Connecticut Agricultural Experiment Station, the Capitol Region and west through the Catskill Mountains to the Bugwood.org Finger Lakes Region, Buffalo and Rochester. In 2017, the first known occurrence in the Adirondack Park was discovered in Lake George. Where does HWA come from? Native to Asia, HWA was introduced to the western United States in the 1920s. It was first observed in the eastern US in 1951 near Richmond, Virginia after an accidental introduction from Japan. HWA has since spread along the East Coast from Georgia to Maine and now occupies nearly half the eastern range of native hemlocks. ▐ What does HWA do to trees? Once hatched, juvenile HWA, known as crawlers, search for suitable sites on the host tree, usually at the base of the needles. They insert their long mouthparts and begin feeding on the tree’s stored starches. -
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”). -
Dry White Pine (Hemlock) Oak Forest
Dry white pine (hemlock) oak forest This community type occurs on fairly dry sites, often with 25% or more of the forest floor covered by rocks, boulders and/or exposed bedrock. The canopy may be somewhat open and tree growth somewhat suppressed. The tree stratum is dominated by a mixture of Pinus strobus (eastern white pine), or occasionally Tsuga canadensis (eastern hemlock), and a mixture of dry-site hardwoods, predominantly oaks. On most sites, the conifer and the hardwood component both range between 25% and 75% of the canopy. The oak species most often associated with this type are Quercus montana (chestnut oak), and Q. alba (white oak), although Q. velutina (black oak), Q. coccinea (scarlet oak), or Q. rubra (northern red oak) may also occur. Other associated trees include Nyssa sylvatica (black-gum), Betula lenta (sweet birch), Fraxinus americana (white ash), Prunus serotina (wild black cherry), and Castanea dentata (American chestnut) sprouts. There is often a heath-dominated shrub layer with Kalmia latifolia (mountain laurel) being especially important; Gaylussacia baccata (black huckleberry), Vaccinium spp. (blueberries), and Kalmia angustifolia (sheep laurel) are also common. Other shrubs, like Cornus florida (flowering dogwood), Hamamelis virginiana (witch-hazel), Viburnum acerifolium (maple-leaved viburnum) may also occur on less acidic sites. There is typically a sparse herbaceous layer with a northern affinity; Aralia nudicaulis (wild sarsaparilla), Pteridium aquilinum (bracken fern), Maianthemum canadense (Canada mayflower), Gaultheria procumbens (teaberry), Trientalis borealis (star-flower), and Medeola virginiana (Indian cumber-root) are typical. The successional status of this type seems variable, in some cases, especially on harsher sites, it appears relatively stable, in other cases it appears to be transitional. -
Common Conifers in New Mexico Landscapes
Ornamental Horticulture Common Conifers in New Mexico Landscapes Bob Cain, Extension Forest Entomologist One-Seed Juniper (Juniperus monosperma) Description: One-seed juniper grows 20-30 feet high and is multistemmed. Its leaves are scalelike with finely toothed margins. One-seed cones are 1/4-1/2 inch long berrylike structures with a reddish brown to bluish hue. The cones or “berries” mature in one year and occur only on female trees. Male trees produce Alligator Juniper (Juniperus deppeana) pollen and appear brown in the late winter and spring compared to female trees. Description: The alligator juniper can grow up to 65 feet tall, and may grow to 5 feet in diameter. It resembles the one-seed juniper with its 1/4-1/2 inch long, berrylike structures and typical juniper foliage. Its most distinguishing feature is its bark, which is divided into squares that resemble alligator skin. Other Characteristics: • Ranges throughout the semiarid regions of the southern two-thirds of New Mexico, southeastern and central Arizona, and south into Mexico. Other Characteristics: • An American Forestry Association Champion • Scattered distribution through the southern recently burned in Tonto National Forest, Arizona. Rockies (mostly Arizona and New Mexico) It was 29 feet 7 inches in circumference, 57 feet • Usually a bushy appearance tall, and had a 57-foot crown. • Likes semiarid, rocky slopes • If cut down, this juniper can sprout from the stump. Uses: Uses: • Birds use the berries of the one-seed juniper as a • Alligator juniper is valuable to wildlife, but has source of winter food, while wildlife browse its only localized commercial value. -
Juniper Mistletoe Minor Effects on Junipers
Juniper Mistletoe Minor effects on junipers Pathogen—Juniper mistletoe (Phoradendron juniperinum) is the only member of the true mistletoes that occurs within the Rocky Mountain Region (fig. 1). Hosts—Within the Rocky Mountain Region, juniper mistletoe is found in the pinyon-juniper woodlands of southwestern Colorado (fig. 2) and can infect all of the juniper species that occur there. Signs and Symptoms—Juniper mistletoe plants are generally densely branched in a spherical pattern and are green to yellow-green (fig. 3). Unlike most true mistletoes that have obvious leaves, juniper mistletoe leaves are greatly reduced, making the plants look similar to, but somewhat larger than, dwarf mistletoes. However, no dwarf mistletoes infect junipers in the Rocky Mountain Region. Disease Cycle—Juniper mistletoe plants are either male or female. The female’s berries are spread by birds that feed on them. As a re- sult, this mistletoe is often found where birds prefer to perch—on the tops of taller trees (fig. 1), near water sources, etc. When the seeds germinate, they penetrate the branch of the host tree. In the branch, the mistletoe forms a root-like structure that is used to gather water and minerals. The plant then produces aerial shoots that produce food Figure 1. Juniper mistletoe plants on one-seed juniper through photosynthesis. in Mesa Verde National Park. Photo: USDA Forest Service. Figure 2. Distribution of juniper mistletoe in the Rocky Mountain Region Figure 3. Closeup of juniper mistletoe on juniper branch. Photo: Robert (from Hawksworth and Scharpf 1981). Mathiasen, Northern Arizona University. Impacts—Impacts associated with juniper mistletoe are generally minor. -
Wakefield 306 2Nd 79500 307 2Nd 71300
WAKEFIELD 306 2ND 79500 307 2ND 71300 405 2ND 56100 406 2ND 81000 409 2ND 8110 508 2ND 124000 302 3RD 83920 303 3RD 131700 304 3RD 112500 305 3RD 25000 306 3RD 139000 307 3RD 56700 308 3RD 58000 403 3RD 10870 405 3RD 35700 501 3RD 144200 503 3RD 17120 704 3RD 33780 804 3RD 920 902 3RD 47800 1600 3RD 15410 1706 3RD 22050 1708 3RD 113870 301 4TH 166700 303 4TH 46400 305 4TH 74900 306 4TH 130300 307 4TH 120300 402 4TH 121900 404 4TH 125800 602 4TH 78100 606 4TH 132500 701 4TH 174540 706 4TH 227000 305 5TH 20500 308 5TH 100970 312 5TH 150800 102 6TH 117950 104 6TH 57100 106 6TH 84360 204 6TH 89200 206 6TH 38200 208 6TH 73900 304 6TH 18490 305 6TH 77130 401 6TH 148000 403 6TH 31750 607 6TH 106500 701 6TH 162000 703 6TH 178500 705 6TH 173300 805 6TH 131900 102 7TH 145000 103 7TH 151500 104 7TH 186800 107 7TH 141500 201 7TH 121200 202 7TH 138300 203 7TH 168900 204 7TH 118800 206 7TH 125500 303 7TH 50600 404 7TH 18170 602 8TH 123100 802 8TH 98700 803 8TH 181400 804 8TH 104900 903 8TH 6080 905 8TH 6080 1001 8TH 6090 1003 8TH 183100 1005 8TH 176700 1007 8TH 167800 1101 8TH 225800 702 9TH 187200 704 9TH 240500 804 9TH 101600 603 10TH 10810 604 10TH 242900 706 10TH 44810 802 10TH 41110 901 10TH 130900 902 10TH 265000 902 10TH 13530 904 10TH 674320 905 10TH 80040 402 BIRCH 79800 403 BIRCH 148900 404 BIRCH 90000 405 BIRCH 107900 406 BIRCH 116100 502 BIRCH 200800 503 BIRCH 145500 504 BIRCH 63000 505 BIRCH 110600 506 BIRCH 216300 602 BIRCH 167600 603 BIRCH 160500 604 BIRCH 96000 605 BIRCH 151100 605 BIRCH 16180 606 BIRCH 6500 607 BIRCH 109300 608 BIRCH -
The World Needs Network Innovation. Juniper Is Here to Help
The world needs network innovation. Juniper is here to help. In a world where the pace of change is accelerating at an unprecedented rate the network has taken on a new level of importance as the vehicle for pulling together our best people, best thinking, and best hope for addressing the critical challenges we face as a global community. The JUNIPER BY THE macro-trends of cloud computing and the mobile Internet NUMBERS hold the potential to expand the reach and power of the network—while creating an explosion of new subscribers, • The world’s top five social media properties new traffic, and new content. In the face of such intense are supported by Juniper demand, this potential cannot be realized with legacy Networks. thinking. Juniper Networks stands as a response and a • The top 10 telecom companies challenge to the traditional approach to the network. in the world run on Juniper Networks. • Juniper Networks is deployed in more than 1,400 national Our Vision government organizations We believe the network is the single greatest vehicle for knowledge, collaboration, and around the world. human advancement that the world has ever known. Now more than ever, the world relies on high-performance networks. And now more than ever, the world needs network • Juniper has over 8,700 innovation to unleash our full potential. employees in 46 worldwide offices, serving over 100 The network plays a central role in addressing the critical challenges we face as a global countries. community. Consider the healthcare industry, where the network is the foundation for new models of mobile affordable care for underserved communities. -
Phylogeny and Biogeography of Tsuga (Pinaceae)
Systematic Botany (2008), 33(3): pp. 478–489 © Copyright 2008 by the American Society of Plant Taxonomists Phylogeny and Biogeography of Tsuga (Pinaceae) Inferred from Nuclear Ribosomal ITS and Chloroplast DNA Sequence Data Nathan P. Havill1,6, Christopher S. Campbell2, Thomas F. Vining2,5, Ben LePage3, Randall J. Bayer4, and Michael J. Donoghue1 1Department of Ecology and Evolutionary Biology, Yale University, New Haven, Connecticut 06520-8106 U.S.A 2School of Biology and Ecology, University of Maine, Orono, Maine 04469-5735 U.S.A. 3The Academy of Natural Sciences, 1900 Benjamin Franklin Parkway, Philadelphia, Pennsylvania 19103 U.S.A. 4CSIRO – Division of Plant Industry, Center for Plant Biodiversity Research, GPO 1600, Canberra, ACT 2601 Australia; present address: Department of Biology, University of Memphis, Memphis, Tennesee 38152 U.S.A. 5Present address: Delta Institute of Natural History, 219 Dead River Road, Bowdoin, Maine 04287 U.S.A. 6Author for correspondence ([email protected]) Communicating Editor: Matt Lavin Abstract—Hemlock, Tsuga (Pinaceae), has a disjunct distribution in North America and Asia. To examine the biogeographic history of Tsuga, phylogenetic relationships among multiple accessions of all nine species were inferred using chloroplast DNA sequences and multiple cloned sequences of the nuclear ribosomal ITS region. Analysis of chloroplast and ITS sequences resolve a clade that includes the two western North American species, T. heterophylla and T. mertensiana, and a clade of Asian species within which one of the eastern North American species, T. caroliniana, is nested. The other eastern North American species, T. canadensis, is sister to the Asian clade. Tsuga chinensis from Taiwan did not group with T. -
Understanding and Developing Resistance in Hemlocks to the Hemlock Woolly Adelgid Author(S): Kelly L.F
Understanding and Developing Resistance in Hemlocks to the Hemlock Woolly Adelgid Author(s): Kelly L.F. Oten, Scott A. Merkle, Robert M. Jetton, Ben C. Smith, Mary E. Talley and Fred P. Hain Source: Southeastern Naturalist, 13(sp6):147-167. Published By: Eagle Hill Institute URL: http://www.bioone.org/doi/full/10.1656/058.013.s610 BioOne (www.bioone.org) is a nonprofit, online aggregation of core research in the biological, ecological, and environmental sciences. BioOne provides a sustainable online platform for over 170 journals and books published by nonprofit societies, associations, museums, institutions, and presses. Your use of this PDF, the BioOne Web site, and all posted and associated content indicates your acceptance of BioOne’s Terms of Use, available at www.bioone.org/page/ terms_of_use. Usage of BioOne content is strictly limited to personal, educational, and non-commercial use. Commercial inquiries or rights and permissions requests should be directed to the individual publisher as copyright holder. BioOne sees sustainable scholarly publishing as an inherently collaborative enterprise connecting authors, nonprofit publishers, academic institutions, research libraries, and research funders in the common goal of maximizing access to critical research. Forest Impacts and Ecosystem Effects of the Hemlock Woolly Adelgid in the Eastern US 2014Southeastern Naturalist 13(Special Issue 6):147–167 Understanding and Developing Resistance in Hemlocks to the Hemlock Woolly Adelgid Kelly L.F. Oten1,*, Scott A. Merkle2, Robert M. Jetton3, Ben C. Smith4, Mary E. Talley4, and Fred P. Hain4 Abstract - In light of the increasing need for long-term, sustainable management for Adel- ges tsugae (Hemlock Woolly Adelgid), researchers are investigating host-plant resistance as part of an integrated approach to combat the pest. -
Hemlock Woolly Adelgid Proceedings
Hemlock Resources in Great Smoky Mountains National Park Glenn Taylor National Park Service, Great Smoky Mountains National Park 107 Park Headquarters Road, Gatlinburg, TN 37738. Abstract Great Smoky Mountains National Park (GRSM), an International Biosphere Reserve and World Heritage Site, encompasses 525,000 acres of the Blue Ridge Mountains of western North Carolina and eastern Tennessee. Of the more than 100 native tree species in forest types ranging from southern yellow pines to Fraser fir, eastern hemlock, Tsuga canadensis (L.) Carr, is the only species of hemlock known within the park. Hemlock is a dominant species in at least five of the twelve vegetation types in GRSM, and it is an associate in most of the others. The extent of the hemlock resource in the Smokies is difficult to measure due to terrain and accessibility, but historical records and recent surveys have provided insight as to how much hemlock was here, how much exists now, and what size and age classes can be found. European settlement and commercial logging had a large impact on the park’s forests. At least 18 commercial logging companies were active on lands that became the park. The Champion Fiber Company harvested 33 million board feet of hemlock in Smokemont, North Carolina between 1920 to1925. The Little River Lumber Company reported that during 1903 to 1939 hemlock accounted for more than 50% of the logs cut. Lambert (1961) estimated that the hemlock harvest from the Little River watershed totaled one billion board feet before cutting stopped. Based on archival records and aerial photo interpretation, Pyle (1985) concluded that 20% of the park was “relatively undisturbed.” This is the basis for determining areas that may not have been cut; however, field checking for verification is essential.