Antimicrobial Properties of Traditional Brewing Herbs
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Caterpillars Moths Butterflies Woodies
NATIVE Caterpillars Moths and utter flies Band host NATIVE Hackberry Emperor oodies PHOTO : Megan McCarty W Double-toothed Prominent Honey locust Moth caterpillar Hackberry Emperor larva PHOTO : Douglas Tallamy Big Poplar Sphinx Number of species of Caterpillars n a study published in 2009, Dr. Oaks (Quercus) 557 Beeches (Fagus) 127 Honey-locusts (Gleditsia) 46 Magnolias (Magnolia) 21 Double-toothed Prominent ( Nerice IDouglas W. Tallamy, Ph.D, chair of the Cherries (Prunus) 456 Serviceberry (Amelanchier) 124 New Jersey Tea (Ceanothus) 45 Buttonbush (Cephalanthus) 19 bidentata ) larvae feed exclusively on elms Department of Entomology and Wildlife Willows (Salix) 455 Larches or Tamaracks (Larix) 121 Sycamores (Platanus) 45 Redbuds (Cercis) 19 (Ulmus), and can be found June through Ecology at the University of Delaware Birches (Betula) 411 Dogwoods (Cornus) 118 Huckleberry (Gaylussacia) 44 Green-briar (Smilax) 19 October. Their body shape mimics the specifically addressed the usefulness of Poplars (Populus) 367 Firs (Abies) 117 Hackberry (Celtis) 43 Wisterias (Wisteria) 19 toothed shape of American elm, making native woodies as host plants for our Crabapples (Malus) 308 Bayberries (Myrica) 108 Junipers (Juniperus) 42 Redbay (native) (Persea) 18 them hard to spot. The adult moth is native caterpillars (and obviously Maples (Acer) 297 Viburnums (Viburnum) 104 Elders (Sambucus) 42 Bearberry (Arctostaphylos) 17 small with a wingspan of 3-4 cm. therefore moths and butterflies). Blueberries (Vaccinium) 294 Currants (Ribes) 99 Ninebark (Physocarpus) 41 Bald cypresses (Taxodium) 16 We present here a partial list, and the Alders (Alnus) 255 Hop Hornbeam (Ostrya) 94 Lilacs (Syringa) 40 Leatherleaf (Chamaedaphne) 15 Honey locust caterpillar feeds on honey number of Lepidopteran species that rely Hickories (Carya) 235 Hemlocks (Tsuga) 92 Hollies (Ilex) 39 Poison Ivy (Toxicodendron) 15 locust, and Kentucky coffee trees. -
LANDFIRE Biophysical Setting Model
LANDFIRE Biophysical Setting Model Biophysical Setting 7316170 Western North American Boreal Shrub and Herbaceous Floodplain Wetland This BPS is lumped with: This BPS is split into multiple models: General Information Contributors (also see the Comments field Date 5/7/2008 Modeler 1 Tina Boucher [email protected] Reviewer Michelle Schuman michelle.schuman@a k.usda.gov Modeler 2 Kori Blankenship [email protected] Reviewer Modeler 3 Colleen Ryan [email protected] Reviewer Vegetation Type Map Zone Model Zone Wetlands/Riparian 73 Alaska N-Cent.Rockies California Pacific Northwest Dominant Species* General Model Sources Great Basin South Central Literature METR3 ERAN6 Great Lakes Southeast Local Data CAAQ MYGA Northeast S. Appalachians EQFL BENA Expert Estimate Northern Plains Southwest COPA28 CHCA2 Geographic Range This system is found throughout the boreal and sub-boreal regions. It occurs within the floodplain boundaries of the Western North American Boreal Montane Floodplain Forest and Shrubland - Boreal, Western North American Boreal Lowland Large River Floodplain Forest and Shrubland and Western North American Boreal Montane Floodplain Forest and Shrubland - Alaska Sub-boreal. Biophysical Site Description The following information was taken from the draft Boreal Ecological Systems description (NatureServe 2008): Floodplain wetlands occur within the active and inactive portions of floodplain systems. Wetlands develop on poorly drained deposits, oxbows and abandoned channels and are often mosaiced with well- drained floodplain vegetation. Vegetation Description Species composition is variable due to diverse environmental conditions such as water depth, substrate and nutrient input, as well as seral stage. Aquatic bed, marsh and fen communities are common. The earliest seral stages (aquatic bed) have aquatic vegetation such as Nuphar polysepala. -
Chemical Composition and Antimicrobial Activity of Fruit Essential Oils of Myrica Gale, a Neglected Non-Wood Forest Product
BALTIC FORESTRY http://www.balticforestry.mi.lt Baltic Forestry 2020 26(1): 13–20 ISSN 1392-1355 Category: research article eISSN 2029-9230 https://doi.org/10.46490/BF423 Chemical composition and antimicrobial activity of fruit essential oils of Myrica gale, a neglected non-wood forest product KRISTINA LOŽIENĖ1,2, JUOZAS LABOKAS1*, VAIDA VAIČIULYTĖ1, JURGITA ŠVEDIENĖ1, VITA RAUDONIENĖ1, ALGIMANTAS PAŠKEVIČIUS1, LAIMA ŠVEISTYTĖ3 AND VIOLETA APŠEGAITĖ1 1 Nature Research Centre, Akademijos g. 2, LT-08412 Vilnius, Lithuania 2 Farmacy Center, Institute of Biomedical Science, Faculty of Medicine, Vilnius University, M.K. Čiurlionio g. 21/27, LT-03101 Vilnius, Lithuania 3 Plant Gene Bank, Stoties g. 2, Akademija, LT-58343 Kėdainių r., Lithuania * Corresponding author: [email protected], phone: +370 5 2729930 Ložienė, K., Labokas, J., Vaičiulytė, V., Švedienė, J., Raudonienė, V., Paškevičius, A., Šveistytė, L. and Apšegaitė, V. 2020. Chemical composition and antimicrobial activity of fruit essential oils of Myrica gale, a neglected non-wood forest product. Baltic Forestry 26(1): 13–20. https://doi.org/10.46490/BF423. Received 18 October 2019 Revised 25 March 2020 Accepted 28 April 2020 Abstract The study aimed to establish the chemical composition of fruit essential oils of M. gale and test their activities against the selected pathogenic bacteria (Staphylococcus aureus, Escherichia coli, Acinetobacter baumannii), yeasts (Candida albicans, C. parapsilosis), fungi (Aspergillus fumigatus, A. flavus) and dermatophytes (Trichophyton rubrum, T. mentagrophytes). Fruit samples from natural (Western Lithuania) and anthropogenic (Eastern Lithuania) M. gale populations were studied separately. Essential oils were isolated from dried fruits by hydrodistillation and analysed by GC/FID and GC/MS methods; enantiomeric composition of α-pinene was established by chiral-phase capillary GC. -
Invasive Trees of Georgia Pub10-14
Pub. No. 39 October 2016 Invasive Trees of Georgia by Dr. Kim D. Coder, Professor of Tree Biology & Health Care Warnell School of Forestry & Natural Resources, University of Georgia Georgia has many species of trees. Some are native trees and some have been introduced from outside the state, nation, or continent. Most of Georgia’s trees are well- behaved and easily develop into sustainable shade and street trees. A few tree species have an extrodinary ability to upsurp resources and take over sites from other plants. These trees are called invasive because they effectively invade sites, many times eliminat- ing other species of plants. There are a few tree species native to Georgia which are considered invasive in other parts of the country. These native invasives, may be well-behaved in Georgia, but reproduce and take over sites elsewhere, and so have gained an invasive status from at least one other invasive species list. Table 1. There are hundreds of trees which have been introduced to Georgia landscapes. Some of these exotic / naturalized trees are considered invasive. The selected list of Georgia invasive trees listed here are notorious for growing rampantly and being difficult to eradicate. Table 2. Table 1: Native trees considered invasive in other parts of the country. scientific name common name scientific name common name Acacia farnesiana sweet acacia Myrica cerifera Southern bayberry Acer negundo boxelder Pinus taeda loblolly pine Acer rubrum red maple Populus deltoides Eastern cottonwood Fraxinus americana white ash Prunus serotina black cherry Fraxinus pennsylvanica green ash Robinia pseudoacacia black locust Gleditsia triacanthos honeylocust Toxicodendron vernix poison sumac Juniperus virginiana eastern redcedar The University of Georgia is committed to principles of equal opportunity and affirmative action. -
Introduction to Common Native & Invasive Freshwater Plants in Alaska
Introduction to Common Native & Potential Invasive Freshwater Plants in Alaska Cover photographs by (top to bottom, left to right): Tara Chestnut/Hannah E. Anderson, Jamie Fenneman, Vanessa Morgan, Dana Visalli, Jamie Fenneman, Lynda K. Moore and Denny Lassuy. Introduction to Common Native & Potential Invasive Freshwater Plants in Alaska This document is based on An Aquatic Plant Identification Manual for Washington’s Freshwater Plants, which was modified with permission from the Washington State Department of Ecology, by the Center for Lakes and Reservoirs at Portland State University for Alaska Department of Fish and Game US Fish & Wildlife Service - Coastal Program US Fish & Wildlife Service - Aquatic Invasive Species Program December 2009 TABLE OF CONTENTS TABLE OF CONTENTS Acknowledgments ............................................................................ x Introduction Overview ............................................................................. xvi How to Use This Manual .................................................... xvi Categories of Special Interest Imperiled, Rare and Uncommon Aquatic Species ..................... xx Indigenous Peoples Use of Aquatic Plants .............................. xxi Invasive Aquatic Plants Impacts ................................................................................. xxi Vectors ................................................................................. xxii Prevention Tips .................................................... xxii Early Detection and Reporting -
Chapter 5: Vegetation of Sphagnum-Dominated Peatlands
CHAPTER 5: VEGETATION OF SPHAGNUM-DOMINATED PEATLANDS As discussed in the previous chapters, peatland ecosystems have unique chemical, physical, and biological properties that have given rise to equally unique plant communities. As indicated in Chapter 1, extensive literature exists on the classification, description, and ecology of peatland ecosystems in Europe, the northeastern United States, Canada, and the Rocky Mountains. In addition to the references cited in Chapter 1, there is some other relatively recent literature on peatlands (Verhoeven 1992; Heinselman 1963, 1970; Chadde et al., 1998). Except for efforts on the classification and ecology of peatlands in British Columbia by the National Wetlands Working Group (1988), the Burns Bog Ecosystem Review (Hebda et al. 2000), and the preliminary classification of native, low elevation, freshwater vegetation in western Washington (Kunze 1994), scant information exists on peatlands within the more temperate lowland or maritime climates of the Pacific Northwest (Oregon, Washington, and British Columbia). 5.1 Introduction There are a number of classification schemes and many different peatland types, but most use vegetation in addition to hydrology, chemistry and topological characteristics to differentiate among peatlands. The subject of this report are acidic peatlands that support acidophilic (acid-loving) and xerophytic vegetation, such as Sphagnum mosses and ericaceous shrubs. Ecosystems in Washington state appear to represent a mosaic of vegetation communities at various stages of succession and are herein referred to collectively as Sphagnum-dominated peatlands. Although there has been some recognition of the unique ecological and societal values of peatlands in Washington, a statewide classification scheme has not been formally adopted or widely recognized in the scientific community. -
Georgia Native Trees Considered Invasive in Other Parts of the Country. Scientific Name Common Name Scientific Name Common Name
Invasive Trees of Georgia Dr. Kim D. Coder, Professor of Tree Biology & Health Care, Warnell School, UGA Georgia has many species of trees. Some are native trees and some have been introduced from outside the state, nation, or continent. Most of Georgia’s trees are well-behaved and easily develop into sustainable shade and street trees. A few tree species have an extrodinary ability to upsurp resources and take over sites from other plants. These trees are called invasive because they effectively invade sites, many times eliminating other species of plants. There are a few tree species native to Georgia which are considered invasive in other parts of the country. These native invasives, may be well-behaved in Georgia, but reproduce and take over sites elsewhere, and so have gained an invasive status from at least one other invasive species list. Table 1. There are hundreds of trees which have been introduced to Georgia landscapes. Some of these exotic / naturalized trees are considered invasive. The selected list of Georgia invasive trees listed here are notorious for growing rampantly and being diffi- cult to eradicate. Table 2. They should not be planted. Table 1: Georgia native trees considered invasive in other parts of the country. scientific name common name scientific name common name Acacia farnesiana sweet acacia Myrica cerifera Southern bayberry Acer negundo boxelder Pinus taeda loblolly pine Acer rubrum red maple Populus deltoides Eastern Fraxinus americana white ash cottonwood Fraxinus pennsylvanica green ash Prunus serotina black cherry Gleditsia triacanthos honeylocust Robinia pseudoacacia black locust Juniperus virginiana eastern Toxicodendron vernix poison sumac redcedar Table 2: Introduced (exotic) tree / shrub species found in Georgia listed at a regional / national level as being ecologically invasive. -
Seed Dispersal and Propagation of Three Myrica Species
Of Birds and Bayberries : Alfred j. Fordham Seed Dispersal and Propagation of Three Myrica Species The genus Myrica comprises about 50 tral United States and from Europe to north- species (often ill-defined) distributed east Asia. throughout the temperate and subtropical All three of these species have nitrogen- areas of both hemispheres. The Arnold Ar- fixing root nodules, which enable them to boretum collection includes three species: thrive m areas where many other plants M. pensylvanica, M. cerifera, andM. gale. could not survive. They are dioecious - Myrica pensylvanica Lois., the common having staminate (male) and pistillate (fe- bayberry or candleberry, occurs naturally male) flowers on different plants - like hol- from Newfoundland to western New York lies and ashes. and Maryland, chiefly in poor soil. It is suck- The fruits of Myrica pensylvanica and M. ering in habit and tends to form shrubby cerifera are small (2.5-3 mm and 3.5~.5 mm clumps, which at maturity can range from 2 in diameter respectively) globose nuts with to 8 feet in height. Frequently it is found on waxlike coatings. It is this waxlike material roadside cuts, railroad banks, gravel pits, and that provides the fragrance in bayberry- other locations where topsoil has been re- scented candles and soap. It becomes bluish moved completely. In Boston its shiny green gray as it dries, making the thickly clustered leaves remain on the branches until No- fruits conspicuous in the landscape. The vember. They are fragrant when crushed, a fruits ripen in late September and are eaten characteristic of all Myrica species. -
The Changing Ground Flora of an Upland Planted Woodland
The changing ground flora of an upland planted woodland John Holland, SRUC Hill & Mountain Research Centre, Kirkton & Auchtertyre Farms SRUC Hill & Mountain Research Centre Loch Lomond & the Trossachs National Park 2 Caol Gleann Gleann a’Chlachain 3 Gleann a’Chlachain Main Woodland (217 ha) 4 Allt Gleann a’Chlachain Gorge Woodland (43 ha) 5 Trees planted in the in the Allt Gleann a‘Chlachain Gorge Woodland and main Gleann a‘Chlachain Woodland (260 ha) Latin Name English Name Total Percentage Betula pubescens Downy Birch 219710 45.35% Betula pendula Silver Birch 63505 13.11% Pinus sylvestris Scot’s Pine 49300 10.18% Alnus glutinosa Common Alder 43765 9.03% Sorbus aucuparia Rowan 38110 7.87% Salix cinerea Grey Willow 23250 4.80% Salix caprea Goat Willow 17505 3.61% Quercus petraea Sessile Oak 8850 1.83% Salix aurita Eared Willow 6250 1.29% Salix mysinifolia Dark-leaved Willow 5010 1.03% Fraxinus excelsior Ash 4060 0.84% Corylus avellana Hazel 3300 0.68% Populus tremula Aspen 1110 0.23% Salix lapponum Downy Willow 750 0.15% Total 484,475 100% 6 7 8 9 10 11 12 Downy Willow (Salix lapponum) 13 14 Vegetation Changes in the Gorge Woodland • Increase in dwarf shrubs, particularly Ling (Calluna vulgaris) • Increase in Bog Myrtle (Myrica gale) 15 Bog Myrtle (Myrica gale) 16 Vegetation Changes in the Gorge Woodland • Increase in dwarf shrubs, particularly Ling (Calluna vulgaris) • Increase in Bog Myrtle (Myrica gale) • Increase in Purple Moor Grass (Molinia caerulea) and a decrease in Mat Grass (Nardus stricta) 17 Scotch Argus (Erebia aethiops) -
St. John Ponds T4 R17 WELS
Ecological Reserve Fact Sheet January 2009 St. John Ponds T4 R17 WELS Vital Statistics Size: 3,887 acres Upland: 3,558 acres Wetlands (NWI): 532 acres Open Water: 329 acres Roads: unimproved-4 miles Biophysical Region: St. John Uplands BPL Region: West Wetland south of Third St. John Pond Rare Species and Exemplary Natural Community Table for St. John Ponds State Common Name Latin Name S-RANK G-RANK Status Exemplary Natural Communities Streamshore Ecosystem S5 GNR N/A Rare Plants Blue-leaved sedge Carex rostrata S2 G5 SC Rare Animals None found Description The upper St. John Ponds include First (Lower and Upper), Second, and Third St. John Ponds and Robinson Pond. Collectively, these water bodies form the headwaters of the St. John River. The Ponds are perched at the top of the watershed, with First St. John Pond over 1800 feet in elevation. Upland forests within the Reserve were heavily harvested in the late 1980s and are now dominated by sapling-stage natural regeneration. A handful of remnant mature pockets exist in riparian areas and along ephemeral streams. In a few small hardwood ravines dominated by sugar maple, several rich-woods “indicator” plants were noted: Braun’s holly fern, snakeroot, doll’s eyes, ostrich fern, and foam-flower. Ecological Reserve Fact Sheet January 2009 Wetlands associated with the Ponds consist of a narrow forested border, some small fringing Spruce –Larch Forested Bogs, and open wetlands. In one forested bog below Third St. John Pond, the trees are mostly 5-10” dbh and there is evidence of a harvest 40+ years ago Robinson Pond and Second St. -
Myrica Cerifera Southern Waxmyrtle1 Edward F
Fact Sheet ST-410 October 1994 Myrica cerifera Southern Waxmyrtle1 Edward F. Gilman and Dennis G. Watson2 INTRODUCTION Multiple, twisted trunks with smooth, light grey bark, aromatic, olive green leaves, and clusters of grey-blue, waxy berries on female plants which are attractive to wildlife are just some of the reasons Southern Waxmyrtle is such a popular landscape plant (Fig. 1). Most specimens form a multi-stemmed, open, rounded canopy of weak trunks and branches. This rapidly-growing, small, evergreen native tree is capable of reaching a height of 25 feet with an equal spread but is usually seen in the 10 to 20-foot range. Sometimes used as a large shrubbery screen, Southern Waxmyrtle is ideal for use as a small tree, the lower limbs removed to reveal its picturesque form. One, or several clustered together, provide pleasing dappled shade for terraces or patios. Figure 1. Middle-aged Southern Waxmyrtle. GENERAL INFORMATION standard; small parking lot islands (< 100 square feet Scientific name: Myrica cerifera in size); narrow tree lawns (3-4 feet wide); specimen; Pronunciation: MEER-ih-kuh ser-IF-er-uh sidewalk cutout (tree pit); residential street tree; no Common name(s): Southern Waxmyrtle, Southern proven urban tolerance Bayberry Availability: generally available in many areas within Family: Myricaceae its hardiness range USDA hardiness zones: 7B through 11 (Fig. 2) Origin: native to North America DESCRIPTION Uses: Bonsai; container or above-ground planter; hedge; large parking lot islands (> 200 square feet in Height: 15 to 25 feet size); wide tree lawns (>6 feet wide); medium-sized Spread: 20 to 25 feet parking lot islands (100-200 square feet in size); Crown uniformity: irregular outline or silhouette medium-sized tree lawns (4-6 feet wide); Crown shape: round; vase shape recommended for buffer strips around parking lots or Crown density: moderate for median strip plantings in the highway; near a deck Growth rate: fast or patio; reclamation plant; screen; trainable as a 1. -
A Field Guide to Selected Trees and Shrubs of the University of Massachusetts Dartmouth Campus
A Field Guide to Selected Trees and Shrubs of the University of Massachusetts Dartmouth Campus Written and Illustrated by: Richard H. Uva Class of 1991 Department of Biology Univeristy of Massachusetts Dartmouth North Dartmouth, MA Edited by: James R. Sears Professor of Biology University of Massachusetts Dartmouth Converted to Web Format by: Sustainability Studies Seminar Class Spring 2012 University of Massachusetts Dartmouth 1 Table of Contents RED MAPLE Ȃ ACER RUBRUM ............................................................................................................. 4 YELLOW BIRCH - BETULA LUTEA ...................................................................................................... 6 GRAY BIRCH - BETULA POPULIFOLIA .............................................................................................. 8 SWEET PEPPERBUSH - CLETHRA ALNIFOLIA .............................................................................. 10 SWEETFERN - COMPTONIA PEREGRINE ........................................................................................ 11 FLOWERING DOGWOOD - CORNUS FLORIDA .............................................................................. 13 AMERICAN BEECH - FAGUS GRANDIFOLIA ................................................................................... 15 WITCH-HAZEL - HAMAMELIS VIRGINIANA ................................................................................... 17 INKBERRY - ILEX GLABRA ................................................................................................................