The Status and Distribution of Tsuga Canadensis (L.) Carr. (Eastern Hemlock) on the Delmarva Peninsula, and the Presence Of
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Survey of the Taxonomic and Tissue Distribution of Microsomal Binding
Survey of the Taxonomic and Tissue Distribution of Microsomal Binding Sites for the Non-Host Selective Fungal Phytotoxin, Fusicoccin Christiane Meyer3, Kerstin Waldkötter3, Annegret Sprenger3, Uwe G. Schlösset, Markus Luther0, and Elmar W. Weiler3 a Lehrstuhl für Pflanzenphysiologie, Ruhr-Universität, D-44780 Bochum, Bundesrepublik Deutschland b Pflanzenphysiologisches Institut (SAG) der Universität, D-37073 Göttingen, Bundesrepublik Deutschland c KFA Jülich, D-52428 Jülich, Bundesrepublik Deutschland Z. Naturforsch. 48c, 595-602(1993); received June 4/July 13, 1993 Vicia faba L., Fusicoccin-Binding Sites. Taxonomie Distribution, Tissue Distribution, Guard Cell Protoplasts The recent identification of the fusicoccin-binding protein (FCBP) in plasma membranes from monocotyledonous and dicotyledonous angiosperms has opened the basis for an elucida tion of the toxin’s mechanism(s) of action and indicated a widespread occurrence of the FCBP in plants. Results of a detailed taxonomic survey of fusicoccin-binding sites are reported. Bind ing sites were not found in prokaryotes, animal tissues, fungi and algae including the most direct extant ancestors of the land plants (Coleochaete). From the Psilotales (Psilophytatae) to the monocotyledonous angiosperms, all taxa analyzed possessed high-affinity microsomal fusicoccin-binding sites. A heterogeneous picture emerged for the Bryophvta. Anthoceros cri- spulus (Anthocerotae), the only hornwort available to study, lacked fusicoccin binding. Within the Hepaticae as well as the Musci, species lacking and species exhibiting toxin binding were found. The binding site thus seems to have emerged very early in the evolution of the land plants. The tissue distribution of fusicoccin-binding sites was studied in Vicia faba L. shoots. All tissues analyzed showed fusicoccin binding, although not to the same extent. -
Field Release of the Leaf-Feeding Moth, Hypena Opulenta (Christoph)
United States Department of Field release of the leaf-feeding Agriculture moth, Hypena opulenta Marketing and Regulatory (Christoph) (Lepidoptera: Programs Noctuidae), for classical Animal and Plant Health Inspection biological control of swallow- Service worts, Vincetoxicum nigrum (L.) Moench and V. rossicum (Kleopow) Barbarich (Gentianales: Apocynaceae), in the contiguous United States. Final Environmental Assessment, August 2017 Field release of the leaf-feeding moth, Hypena opulenta (Christoph) (Lepidoptera: Noctuidae), for classical biological control of swallow-worts, Vincetoxicum nigrum (L.) Moench and V. rossicum (Kleopow) Barbarich (Gentianales: Apocynaceae), in the contiguous United States. Final Environmental Assessment, August 2017 Agency Contact: Colin D. Stewart, Assistant Director Pests, Pathogens, and Biocontrol Permits Plant Protection and Quarantine Animal and Plant Health Inspection Service U.S. Department of Agriculture 4700 River Rd., Unit 133 Riverdale, MD 20737 Non-Discrimination Policy The U.S. Department of Agriculture (USDA) prohibits discrimination against its customers, employees, and applicants for employment on the bases of race, color, national origin, age, disability, sex, gender identity, religion, reprisal, and where applicable, political beliefs, marital status, familial or parental status, sexual orientation, or all or part of an individual's income is derived from any public assistance program, or protected genetic information in employment or in any program or activity conducted or funded by the Department. (Not all prohibited bases will apply to all programs and/or employment activities.) To File an Employment Complaint If you wish to file an employment complaint, you must contact your agency's EEO Counselor (PDF) within 45 days of the date of the alleged discriminatory act, event, or in the case of a personnel action. -
"National List of Vascular Plant Species That Occur in Wetlands: 1996 National Summary."
Intro 1996 National List of Vascular Plant Species That Occur in Wetlands The Fish and Wildlife Service has prepared a National List of Vascular Plant Species That Occur in Wetlands: 1996 National Summary (1996 National List). The 1996 National List is a draft revision of the National List of Plant Species That Occur in Wetlands: 1988 National Summary (Reed 1988) (1988 National List). The 1996 National List is provided to encourage additional public review and comments on the draft regional wetland indicator assignments. The 1996 National List reflects a significant amount of new information that has become available since 1988 on the wetland affinity of vascular plants. This new information has resulted from the extensive use of the 1988 National List in the field by individuals involved in wetland and other resource inventories, wetland identification and delineation, and wetland research. Interim Regional Interagency Review Panel (Regional Panel) changes in indicator status as well as additions and deletions to the 1988 National List were documented in Regional supplements. The National List was originally developed as an appendix to the Classification of Wetlands and Deepwater Habitats of the United States (Cowardin et al.1979) to aid in the consistent application of this classification system for wetlands in the field.. The 1996 National List also was developed to aid in determining the presence of hydrophytic vegetation in the Clean Water Act Section 404 wetland regulatory program and in the implementation of the swampbuster provisions of the Food Security Act. While not required by law or regulation, the Fish and Wildlife Service is making the 1996 National List available for review and comment. -
The Distribution and Habitat Selection of Introduced Eastern Grey Squirrels, Sciurus Carolinensis, in British Columbia
03_03045_Squirrels.qxd 11/7/06 4:25 PM Page 343 The Distribution and Habitat Selection of Introduced Eastern Grey Squirrels, Sciurus carolinensis, in British Columbia EMILY K. GONZALES Centre for Applied Conservation Research, University of British Columbia, Forest Sciences Centre, 3004-2424 Main Mall, Vancouver, British Columbia V6T 1Z4 Canada Gonzales, Emily K. 2005. The distribution and habitat selection of introduced Eastern Grey Squirrels, Sciurus carolinensis,in British Columbia. Canadian Field-Naturalist 119(3): 343-350. Eastern Grey Squirrels were first introduced to Vancouver in the Lower Mainland of British Columbia in 1909. A separate introduction to Metchosin in the Victoria region occurred in 1966. I surveyed the distribution and habitat selection of East- ern Grey Squirrels in both locales. Eastern Grey Squirrels spread throughout both regions over a period of 30 years and were found predominantly in residential land types. Some natural features and habitats, such as mountains, large bodies of water, and coniferous forests, have acted as barriers to expansion for Eastern Grey Squirrels. Given that urbanization is replacing conifer forests throughout southern British Columbia, it is predicted that Eastern Grey Squirrels will continue to spread as habitat barriers are removed. Key Words: Eastern Grey Squirrels, Sciurus carolinensis, distribution, habitat selection, invasive, British Columbia. The vast majority of introduced species do not suc- such as backyards, parks, and cemeteries (Pasitschniak- cessfully establish populations in novel environments Arts and Bendell 1990). EGS co-occur with North (Williamson 1996). Many successful non-native species American Red Squirrels (Tamiasciurus hudsonicus) are human comensals which thrive in human-modified throughout much of their range where habitat special- environments (Williamson and Fitter 1996; Sax and ization and not competition determines the differences Brown 2000). -
November 27,2014 Available Description Potsize 4 Abies Alba
November 27,2014 Available Description Potsize 4 Abies alba Barabit's Spreader- std 24"hd #3 8 Abies alba Pendula #2 4 Abies alba Pendula #3 2 Abies alba Pendula #5 13 Abies alba Pyramidalis #3 213 Abies balsamea Nana #1 8 Abies balsamea Prostrata- std 18"hd #3 5 Abies balsamea Prostrata- std 2' #3 10 Abies cephalonica Meyer's Dwarf- std 18"hd #3 2 Abies concolor Blue Cloak #3 15 Abies concolor Candicans #3 8 Abies delavayi Herford #5 2 Abies forestii var. Forestii #5 20 Abies fraseri Klein's Nest- std 18"hd #3 28 Abies homolepis Tomomi- std 18"hd #3 11 Abies John's Pool #5 5 Abies koreana Gelbunt #1 7 Abies koreana Green Carpet #5 2 Abies koreana Oberon -std #3 2 Abies lasiocarpa Green Globe- 12" std #3 24 Abies lasiocarpa Green Globe #3 3 Abies nordmanniana Munsterland- std 18"hd #3 3 Abies nordmanniana Trautmann #5 2 Abies pinsapo Glauca #1 6 Abies pinsapo Glauca Nana #3 2 Abies procera Blaue Hexe- std 8"hd #3 4 Abies procera Prostrata #3 5 Abies procera Sherwoodii #3 5 Abies procera Sherwoodii #5 8 Abies veitchii Olivaceae #3 3 Abies veitchii var. Olivaceae #5 6 Acer griseum #3 1 Acer griseum #7 47 Acer griseum- 6'tall #5 14 Albizzia julibrissin #3 1 Albizzia julibrissin Summer Chocolate #3 5 Buxus microphylla John Baldwin #3 840 Buxus microphylla John Baldwin #1 20 Buxus sempervirens Faulkner #3 1 Buxus sempervirens Green Velvet #3 10 Buxus sempervirens Raket #3 263 Buxus sempervirens Suffruticosa #1 100 Buxus sempervirens Vardar Valley #1 185 Buxus sinica var. -
Survey of Aquatic Invasive Species in Maryland Lakes
Survey of Aquatic Invasive Species in Maryland Lakes Report of Survey Activity and Results January 2018 Prepared For Maryland State Legislature Maryland Department of Natural Resources Maryland Park Service Maryland Fishing and Boating Service Prepared by Mark Lewandowski and Mike Naylor Appendix A. by Cathy Wazniak and Celia Dawson Maryland Department of Natural Resources Resource Assessment Service Tidewater Ecosystem Assessment 1 Table of Contents Executive Summary Page 3 Report Page 3 Figure 1- Map of State Lakes Page 5 Lake Survey Findings New Germany Lake Page 6 Tuckahoe Lake Page 7 Myrtle Grove Lake Page 8 Blairs Valley Lake Page 9 Urieville Mill Pond Page 10 Greenbriar Lake Page 11 Hunting Creek Lake Page 12 Smithville Lake Page 13 Unicorn Lake Page 14 Wye Mills Lake Page 15 Herrington Lake Page 16 Clopper Lake Page 17 Lake Habeeb Page 18 St. Mary’s Lake Page 19 Savage River Reservoir Page 20 Deep Creek Lake Page 21 Recommendations Page 22 Table 1- SAV, Emergent Plant and Floating Plant Summary Page 24 Appendix A- Algae Synopsis Page 26 2 Executive Summary Biologists from DNR’s Resource Assessment Service conducted the first Aquatic Invasive Species survey in all sixteen state -owned lakes in the summer of 2016. Surveys were conducted from kayaks, canoes and motor boats to assess the aquatic macrophyte communities in each lake. The purpose of the survey was to assess the current condition of the state lakes and assist in making management decisions related to aquatic invasive species. Overall, twenty-nine species of submerged aquatic vegetation and six species of floating or emergent plants were observed. -
Susceptibility of Larch, Hemlock, Sitka Spruce, and Douglas-Fir to Phytophthora Ramorum1
Proceedings of the Sudden Oak Death Fifth Science Symposium Susceptibility of Larch, Hemlock, Sitka Spruce, and 1 Douglas-fir to Phytophthora ramorum Gary Chastagner,2 Kathy Riley,2 and Marianne Elliott2 Introduction The recent determination that Phytophthora ramorum is causing bleeding stem cankers on Japanese larch (Larix kaempferi (Lam.) Carrière) in the United Kingdom (Forestry Commission 2012, Webber et al. 2010), and that inoculum from this host appears to have resulted in disease and canker development on other conifers, including western hemlock (Tsuga heterophylla (Raf.) Sarg.), Douglas-fir (Pseudotsuga menziesii (Mirb.) Franco), grand fir (Abies grandis (Douglas ex D. Don) Lindl.), and Sitka spruce (Picea sitchensis (Bong.) Carrière), potentially has profound implications for the timber industry and forests in the United States Pacific Northwest (PNW). A clearer understanding of the susceptibility of these conifers to P. ramorum is needed to assess the risk of this occurring in the PNW. Methods An experiment was conducted to examine the susceptibility of new growth on European (L. decidua Mill.), Japanese, eastern (L. laricina (Du Roi) K. Koch), and western larch (L. occidentalis Nutt.); western and eastern hemlock (T. canadensis (L.) Carrière); Sitka spruce; and a coastal seed source of Douglas-fir to three genotypes (NA1, NA2, and EU1) of P. ramorum in 2011. In 2012, a similar experiment was conducted using only the four larch species. Container-grown seedlings or saplings were used in all experiments. Five trees or branches of each species were inoculated with a single isolate of the three genotypes by spraying the foliage with a suspension of zoospores (105/ml). -
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”). -
Western Larch, Which Is the Largest of the American Larches, Occurs Throughout the Forests of West- Ern Montana, Northern Idaho, and East- Ern Washington and Oregon
Forest An American Wood Service Western United States Department of Agriculture Larch FS-243 The spectacular western larch, which is the largest of the American larches, occurs throughout the forests of west- ern Montana, northern Idaho, and east- ern Washington and Oregon. Western larch wood ranks among the strongest of the softwoods. It is especially suited for construction purposes and is exten- sively used in the manufacture of lumber and plywood. The species has also been used for poles. Water-soluble gums, readily extracted from the wood chips, are used in the printing and pharmaceutical industries. F–522053 An American Wood Western Larch (Lark occidentalis Nutt.) David P. Lowery1 Distribution Western larch grows in the upper Co- lumbia River Basin of southeastern British Columbia, northeastern Wash- ington, northwest Montana, and north- ern and west-central Idaho. It also grows on the east slopes of the Cascade Mountains in Washington and north- central Oregon and in the Blue and Wallowa Mountains of southeast Wash- ington and northeast Oregon (fig. 1). Western larch grows best in the cool climates of mountain slopes and valleys on deep porous soils that may be grav- elly, sandy, or loamy in texture. The largest trees grow in western Montana and northern Idaho. Western larch characteristically occu- pies northerly exposures, valley bot- toms, benches, and rolling topography. It occurs at elevations of from 2,000 to 5,500 feet in the northern part of its range and up to 7,000 feet in the south- ern part of its range. The species some- times grows in nearly pure stands, but is most often found in association with other northern Rocky Mountain con- ifers. -
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. -
An Ecological Classification of Groundwater-Fed
ECOLOGICAL CLASSIFICATION OF GROUNDWATER-FED SEEPAGE WETLANDS OF THE MARYLAND COASTAL PLAIN By Jason W. Harrison Wildlife and Heritage Service Maryland Department of Natural Resources 909 Wye Mills Rd. Wye Mills, Maryland 21679 410-827-8612 ext. 109 [email protected] Wesley M. Knapp Wildlife and Heritage Service Maryland Department of Natural Resources 909 Wye Mills Rd. Wye Mills, Maryland 21679 410-827-8612 ext. 100 [email protected] June 2010 (updated February 2015) Prepared for United States Fish and Wildlife Service Lawrence J. Hogan, Jr. Governor Boyd K. Rutherford Lt. Governor Mark J. Belton Acting Secretary The facilities and services of the Maryland Department of Natural Resources are available to all without regard to race, color, religion, sex, sexual orientation, age, national origin or physical or mental disability. This document is available in an alternative format upon request from a qualified individual with a disability. Toll free in Maryland: 1-877-620-8DNR ext. 3 Out of State call: 1-410-260-8540 TTY users call via the MD Relay www.dnr.maryland.gov Printed on recycled paper Citation: Harrison, J.W., W.M. Knapp. 2010. Ecological classification of groundwater-fed wetlands of the Maryland Coastal Plain. Maryland Department of Natural Resources, Wildlife and Heritage Service, Natural Heritage Program, Annapolis, MD. June 2010. 98 pp. 2 TABLE OF CONTENTS LIST OF FIGURES ..............................................................................................................................................