Picea Rubens Sarg. Red Spruce
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Natural Communities of Michigan: Classification and Description
Natural Communities of Michigan: Classification and Description Prepared by: Michael A. Kost, Dennis A. Albert, Joshua G. Cohen, Bradford S. Slaughter, Rebecca K. Schillo, Christopher R. Weber, and Kim A. Chapman Michigan Natural Features Inventory P.O. Box 13036 Lansing, MI 48901-3036 For: Michigan Department of Natural Resources Wildlife Division and Forest, Mineral and Fire Management Division September 30, 2007 Report Number 2007-21 Version 1.2 Last Updated: July 9, 2010 Suggested Citation: Kost, M.A., D.A. Albert, J.G. Cohen, B.S. Slaughter, R.K. Schillo, C.R. Weber, and K.A. Chapman. 2007. Natural Communities of Michigan: Classification and Description. Michigan Natural Features Inventory, Report Number 2007-21, Lansing, MI. 314 pp. Copyright 2007 Michigan State University Board of Trustees. Michigan State University Extension programs and materials are open to all without regard to race, color, national origin, gender, religion, age, disability, political beliefs, sexual orientation, marital status or family status. Cover photos: Top left, Dry Sand Prairie at Indian Lake, Newaygo County (M. Kost); top right, Limestone Bedrock Lakeshore, Summer Island, Delta County (J. Cohen); lower left, Muskeg, Luce County (J. Cohen); and lower right, Mesic Northern Forest as a matrix natural community, Porcupine Mountains Wilderness State Park, Ontonagon County (M. Kost). Acknowledgements We thank the Michigan Department of Natural Resources Wildlife Division and Forest, Mineral, and Fire Management Division for funding this effort to classify and describe the natural communities of Michigan. This work relied heavily on data collected by many present and former Michigan Natural Features Inventory (MNFI) field scientists and collaborators, including members of the Michigan Natural Areas Council. -
Edna Assay Development
Environmental DNA assays available for species detection via qPCR analysis at the U.S.D.A Forest Service National Genomics Center for Wildlife and Fish Conservation (NGC). Asterisks indicate the assay was designed at the NGC. This list was last updated in June 2021 and is subject to change. Please contact [email protected] with questions. Family Species Common name Ready for use? Mustelidae Martes americana, Martes caurina American and Pacific marten* Y Castoridae Castor canadensis American beaver Y Ranidae Lithobates catesbeianus American bullfrog Y Cinclidae Cinclus mexicanus American dipper* N Anguillidae Anguilla rostrata American eel Y Soricidae Sorex palustris American water shrew* N Salmonidae Oncorhynchus clarkii ssp Any cutthroat trout* N Petromyzontidae Lampetra spp. Any Lampetra* Y Salmonidae Salmonidae Any salmonid* Y Cottidae Cottidae Any sculpin* Y Salmonidae Thymallus arcticus Arctic grayling* Y Cyrenidae Corbicula fluminea Asian clam* N Salmonidae Salmo salar Atlantic Salmon Y Lymnaeidae Radix auricularia Big-eared radix* N Cyprinidae Mylopharyngodon piceus Black carp N Ictaluridae Ameiurus melas Black Bullhead* N Catostomidae Cycleptus elongatus Blue Sucker* N Cichlidae Oreochromis aureus Blue tilapia* N Catostomidae Catostomus discobolus Bluehead sucker* N Catostomidae Catostomus virescens Bluehead sucker* Y Felidae Lynx rufus Bobcat* Y Hylidae Pseudocris maculata Boreal chorus frog N Hydrocharitaceae Egeria densa Brazilian elodea N Salmonidae Salvelinus fontinalis Brook trout* Y Colubridae Boiga irregularis Brown tree snake* -
EASTERN SPRUCE an American Wood
pÍ4 .4 . 1j%4 Mk ,m q ' ' 5 -w +*' 1iiL' r4i41. a')' q I Figure 1.-Range of white spruce (Picea glauca). 506612 2 EASTERN SPRUCE an American wood M.D. Ostrander' DISTRIBUTION monly found in cold, poorly-drained bogs throughout its range, and under such conditions forms dense slow- (Moench) Three spruces-white (Picea glauca growing pure stands. Through most of its range black Voss) , black (Picea , mariana (Mill.) B.S.P.) and red spruce occurs at elevations between 500 and 2,500 Picea rubens collectively known east- ( Sarg.)-are as feet, although substantial stands occur at lower eleva- em spruce. The natural range of white spruce ex- tions in eastern Canada. In the Canadian Rockies and tends from Newfoundland and Labrador west across Alaska it grows up the slopes to the limits of tree Canada to northwestern Alaska and southward growth. It usually is found in pure stands and in mix- through northern New England, New York, Mich- tures with other lowland softwoods, aspen, and birch. igan, Wisconsin, and Minnesota (fig. In western i ) . The natural range of red spruce extends from the mountains in Canada it is found east of coastal Nova Scotia and New Brunswick in Canada, southward British Columbia. Outlying stands also occur in the through New England and eastern New York. It con- Black Hills of South Dakota and in Montana and tinues southward at high elevations in the Appala. Wyoming. White spruce grows under a variety of chian Mountains to western North Carolina and east- climatic conditions, ranging from the wet insular cli- em Tennessee (fig. -
Growth Pattern of Picea Rubens Prior to Canopy Recruitment
pr7 7 AL Plant Ecology 140: 245-253, 1999. 245 rim © 1999 Kluwer Academic Publishers. Printed in the Netherlands. Growth pattern of Picea rubens prior to canopy recruitment Xinyuan Wu l , J. Frank McCormick2 Richard T. Busing3 1 Department of Rangeland Ecology and Management Texas AM University, College Station, TX 77843, USA; 2Department of Ecology and Evolutionary Biology, The University of Tennessee Knoxville, TN 37996, USA; 3Forestry Sciences Laboratory 3200 SW Jefferson Way Corvallis, OR 97331, USA Received 22 July 1997; accepted in revised form 6 October 1998 Key words: Canopy disturbance regime, Great Smoky Mountains, Radial growth, Red spruce, Suppression and release Abstract A majority (72%) of Picea rubens Sarg. (red spruce) trees in an old-growth spruce-fir forest in the Great Smoky Mountains underwent episodes of radial growth suppression and release before they reached the forest canopy. Prior to canopy recruitment, trees experienced an average of 1.43 and a maximum of 7 suppression periods with an average ring width of 0.257 mm. Duration of suppression periods ranged from 4 to 79 years with an average of 19.05 years, which was significantly shorter than the average duration of release periods (29.00 years). Mean ring width in a suppression period was negatively correlated with duration of the suppression period. The opposite was true for release periods. The severity of suppression had no significant effect on mean ring width in subsequent release periods. Greater suppression was observed in the recent growth pattern of current non-canopy trees than in the historical growth pattern reconstructed from current canopy trees. -
Abstract Walker-Lane, Laura Newman
ABSTRACT WALKER-LANE, LAURA NEWMAN. The Effect of Hemlock Woolly Adelgid Infestation on Water Relations of Carolina and Eastern Hemlock. (Under the direction of John Frampton.) In North America, hemlock woolly adelgid (HWA; Adelges tsugae Annand) is an exotic insect pest from Asia that is causing severe decimation of native eastern hemlock (Tsuga canadensis (L.) Carr.) and Carolina hemlock (Tsuga caroliniana Engelm.). Extensive research has been committed to the ecological impacts and potential control measures of HWA, but the exact physiological mechanisms that cause tree decline and mortality are not known. Eastern and Carolina hemlock may be reacting to infestation in a manner similar to the response of Fraser fir (Abies fraseri (Pursh.) Poir.) to infestation by balsam woolly adelgid (BWA; Adelges picea Ratz.). It is known that Fraser fir produces abnormal xylem in response to BWA feeding. This abnormal xylem obstructs water movement within the trees, causing Fraser fir to die of water-stress. In this study, water relations within 15 eastern and Carolina hemlock were evaluated to determine if infestation by HWA was causing water-stress. Water potential, carbon-13 isotope ratio, stem conductivity, and stomatal conductance measurements were conducted on samples derived from those trees. In addition, branch samples were analyzed for possible wood anatomy alterations as a result of infestation. Pre-dawn branch water potential (Ψ) measurements were more negative in infested hemlock than in non-infested trees. Carbon isotope ratios (normalized δ13C vs. VPDB) of the branches were more positive for infested trees, while stomatal conductance (gs) was lower in infested trees. These results indicate that infested eastern and Carolina hemlock are experiencing drought-like symptoms. -
Population Isolation Results in Unexpectedly High Differentiation in Carolina Hemlock (Tsuga Caroliniana), an Imperiled Southern Appalachian Endemic Conifer
Tree Genetics & Genomes (2017) 13:105 DOI 10.1007/s11295-017-1189-x ORIGINAL ARTICLE Population isolation results in unexpectedly high differentiation in Carolina hemlock (Tsuga caroliniana), an imperiled southern Appalachian endemic conifer Kevin M. Potter1 & Angelia Rose Campbell2 & Sedley A. Josserand3 & C. Dana Nelson3,4 & Robert M. Jetton5 Received: 16 December 2016 /Revised: 14 August 2017 /Accepted: 10 September 2017 # US Government (outside the USA) 2017 Abstract Carolina hemlock (Tsuga caroliniana Engelm.) is a range-wide sampling of the species. Data from 12 polymor- rare conifer species that exists in small, isolated populations phic nuclear microsatellite loci were collected and analyzed within a limited area of the Southern Appalachian Mountains for these samples. The results show that populations of of the USA. As such, it represents an opportunity to assess Carolina hemlock are extremely inbred (FIS =0.713)andsur- whether population size and isolation can affect the genetic prisingly highly differentiated from each other (FST =0.473) diversity and differentiation of a species capable of long- with little gene flow (Nm = 0.740). Additionally, most popu- distance gene flow via wind-dispersed pollen and seed. This lations contained at least one unique allele. This level of dif- information is particularly important in a gene conservation ferentiation is unprecedented for a North American conifer context, given that Carolina hemlock is experiencing mortality species. Numerous genetic clusters were inferred using two throughout -
Identifying and Managing Christmas Tree Diseases, Pests, and Other Problems Luisa Santamaria Chal Landgren
PNW 659 ∙ April 2014 Identifying and Managing Christmas Tree Diseases, Pests, and Other Problems Luisa Santamaria Chal Landgren A Pacific Northwest Extension Publication Oregon State University ∙ University of Idaho ∙ Washington State University AUTHORS & ACKNOWLEDGMENTS Luisa Santamaria, assistant professor, Extension plant pathologist in nursery crops; and Chal Landgren, professor, Extension Christmas tree specialist; both of Oregon State University. The authors thank the following peers for the review of these diagnostic cards and for their helpful comments and suggestions. In alphabetical order: • Michael Bondi–Oregon State University • Gary Chastagner–Washington State University • Rick Fletcher–Oregon State University • Alina Freire-Fierro–Drexel University • Carla Garzon–Oklahoma State University • Dionisia Morales–Oregon State University • Kathy Riley–Washington State University • Helmuth Rogg–Oregon Department of Agriculture • David Shaw–Oregon State University • Cathy E. Thomas–Pennsylvania Department of Agriculture • Luis Valenzuela–Oregon State University This project was funded by the USDA Specialty Crop Block Grant program (grant numbers ODA-2577-GR and ODA-3557-GR). TABLE OF CONTENTS Diseases Damage (Weather) Annosus Root Rot . .1-2 Frost Damage . 43 Phytophthora Root Rot . .3-4 Winter Injury . 44 Grovesiella Canker . .5-6 Drought . 45 Interior Needle Blight . .7-8 Heat Damage . 46 Rhabdocline Needle Cast . .9-10 Swiss Needle Cast . 11-12 Damage (Chemical) Melampsora Needle Rust . 13-14 2,4-D and triclopyr . 47 Pucciniastrum Needle Rust . 15-16 Fertilizer Burn . 48 Uredinopsis Needle Rust . 17-18 Glyphosate (Roundup) . 49 Triazines . 50 Insects Twig Aphid . 19-20 Damage (Vertebrate) Conifer Root Aphid . 21-22 Deer, Elk, Mice, & Voles . 51 Conifer Aphids . 23-24 Rabbits & Birds . 52 Balsam Woolly Adelgid . -
Biology and Management of Balsam Twig Aphid
Extension Bulletin E-2813 • New • July 2002 Biology and Management of Balsam Twig Aphid Kirsten Fondren Dr. Deborah G. McCullough Research Assistant Associate Professor Dept. of Entomology Dept. of Entomology and Michigan State University Dept. of Forestry Michigan State University alsam twig aphid (Mindarus abietinus MICHIGAN STATE aphids will also feed on other true firs, Koch) is a common and important UNIVERSITY including white fir (A. concolor) and B insect pest of true fir trees (Fig. 1). Canaan fir (A. balsamea var. phanerolepsis), This bulletin is designed to help you EXTENSION especially if they are growing near balsam recognize and manage balsam twig aphid in or Fraser fir trees. Christmas tree plantations. Knowing the biology of this aphid will help you to plan scouting and Biology control activities, evaluate the extent of damage caused by Balsam twig aphid goes through three generations every aphid feeding and identify the aphid’s natural enemies. year. The aphids overwinter as eggs on needles near the Using an integrated management program will help you to bases of buds. Eggs begin to hatch early in spring, typically control balsam twig aphid efficiently and effectively. around late March to mid-April, depending on temperatures and location within the state. Hatching is completed in one to two weeks. Recent studies in Michigan showed that egg Photo by M. J. Higgins. hatch began at roughly 60 to 70 degree-days base 50 degrees F (DD50) and continued until approximately 100 DD50 (see degree-days discussion under “Timing insecticide sprays” on p. 5). The newly hatched aphids are very small and difficult to see, but by mid- to late April, at approximately 100 to 140 DD50, they have grown enough to be easily visible against a dark background. -
Picea Rubens Sarg. Family: Pinaceae Red Spruce
Picea rubens Sarg. Family: Pinaceae Red Spruce The genus Picea is composed of about 30 species native to North America [12] and Eurasia [20]. The word picea comes from the ancient Latin name (pix, picis = pitch) of a pitchy pine, probably Scotch pine (Pinus sylvestris L.). The word rubens means reddish, referring to the reddish brown cones. Other Common Names: Abetina rossa, Adirondack spruce, black spruce, blue spruce, Canadese rode spar, Canadian red spruce, Canadian spruce, double spruce, eastern spruce, epicea rouge du Canada, he balsam, he- balsam, Hudson-fichte, kanadensisk rod-gran, North American red spruce, picea roja de Canada, picea rossa del Canada, red spruce, rot-fichte, sapinette rouge du Canada, spruce pine, spruces d'america, West Virginia spruce, yellow spruce. Distribution: Red spruce is native to Cape Breton Islands, Nova Scotia and New Brunswick, west to Maine, southern Quebec and southeastern Ontario and south to central New York, northeastern Pennsylvania, northern New Jersey and Massachusetts. It also grows in the Appalachian Mountains of extreme western Maryland, eastern West Virginia, northern and western Virginia, western North Carolina and eastern Tennessee. The Tree: Red spruce can reach heights of 110 feet, with diameters of 4.5 feet. At the northern limit of its range, red spruce reaches heights of only 80 feet and diameters of 2 feet. General Wood Characteristics: The wood dries easily and is stable after drying, is moderately light in weight and easily worked, has moderate shrinkage, and is moderately strong, stiff, tough, and hard. It is not very resistant to bending or end-wise compression. -
Measuring Restoration Success CASRI Partnership VIRTUAL Conference 2020
Measuring Restoration Success CASRI Partnership VIRTUAL Conference 2020 November 4 – 5, 2020 CASRI's 2020 "Measuring Restoration Success" conference will focus on quantitative and qualitative measures of success for restoration of the red spruce-northern hardwood ecosystem in Central Appalachia. Decades of boots-on-the-ground restoration actions and associated research and monitoring has resulted in quantifiable success stories and lessons learned, all of which provide important knowledge to inform future actions and approaches. This conference gathers managers, practitioners, scientists, and leaders in the field to discuss the latest research findings, problem-solve common management challenges, and network to advance new and emerging partnerships. Strong partnerships will enable the network to continue to advance landscape resilience and connectivity of red spruce forests across the region. SCHEDULE Wednesday November 4, 2020 --- ZOOM link Day 1 Time Topic Speaker 9:00 – 9:10 Welcome and housekeeping Katy Barlow 9:10 – 9:50 Keynote Presentation: Are We Hitting the Mark Jamie Schuler for Red Spruce Restoration? Session 1: History of CASRI 10:00 – 10:15 The Blister Swamp Conservation and Alton Byers Restoration Project Twenty Years Later 10:15 – 10:30 Red spruce in West Virginia: Early Reports James Rentch from A. D. Hopkins and the W.Va. Agricultural Experiment Station 10:30 – 10:45 Session 1 Discussion Panel Session 2: Soils and Vegetation 11:00 – 11:10 Informed Red Spruce Restoration and James Leonard Conservation Planning using Soil -
Evaluating the Invasive Potential of an Exotic Scale Insect Associated with Annual Christmas Tree Harvest and Distribution in the Southeastern U.S
Trees, Forests and People 2 (2020) 100013 Contents lists available at ScienceDirect Trees, Forests and People journal homepage: www.elsevier.com/locate/tfp Evaluating the invasive potential of an exotic scale insect associated with annual Christmas tree harvest and distribution in the southeastern U.S. Adam G. Dale a,∗, Travis Birdsell b, Jill Sidebottom c a University of Florida, Entomology and Nematology Department, Gainesville, FL 32611 b North Carolina State University, NC Cooperative Extension, Ashe County, NC c North Carolina State University, College of Natural Resources, Mountain Horticultural Crops Research and Extension Center, Mills River, NC 28759 a r t i c l e i n f o a b s t r a c t Keywords: The movement of invasive species is a global threat to ecosystems and economies. Scale insects (Hemiptera: Forest entomology Coccoidea) are particularly well-suited to avoid detection, invade new habitats, and escape control efforts. In Fiorinia externa countries that celebrate Christmas, the annual movement of Christmas trees has in at least one instance been Elongate hemlock scale associated with the invasion of a scale insect pest and subsequent devastation of indigenous forest species. In the Conifers eastern United States, except for Florida, Fiorinia externa is a well-established exotic scale insect pest of keystone Fraser fir hemlock species and Fraser fir Christmas trees. Annually, several hundred thousand Fraser firs are harvested and shipped into Florida, USA for sale to homeowners and businesses. There is concern that this insect may disperse from Christmas trees and establish on Florida conifers of economic and conservation interest. Here, we investigate the invasive potential of F. -
The Incidence of Dwarf Mistletoe in Minnesota Black Spruce Stands Detected by Operational Inventories
The Incidence of Dwarf Mistletoe in Minnesota Black Spruce Stands Detected by Operational Inventories Fred Baker, Mark Hansen, John D. Shaw, Manfred Mielke, and Dixon Shelstad We surveyed black spruce stands within 0.5 miles of US Forest Service Forest Inventory and Analysis (FIA) plots and compared dwarf mistletoe status with that of the FIA and Minnesota Department of Natural Resources (DNR) forest inventories. Our results differed from FIA results in 3 of 16 stands with FIA plots, with FIA most often not recording dwarf mistletoe in infested stands. The infestation status of 140 of 202 surrounding stands was the same as recorded for the nearby FIA plot. Minnesota DNR forest inventory identified dwarf mistletoe in only 26 of 112 infested stands. Using only the most recent FIA plot data, 8% of FIA plots were recorded as infested. Considering an FIA plot to be infested if it was infested at any time in its history raises the percentage of infested FIA plots to 11%. Of the stands we surveyed, 112 of 202 (55%) were infested, but spatial autocorrelation may bias our sample. For the infested stands, dwarf ABSTRACT mistletoe is projected to infest 20% of the stand area and reduce timber volume by at least 14% in the current rotation. Keywords: disease survey he eastern spruce dwarf mistletoe (Arceuthobium pusillum) ventory plots are often unreliable (See Muir and Moody 2002 and causes the most important black spruce (Picea mariana) dis- references therein), in at least one case dwarf mistletoe incidence Tease throughout the range of the species. Anderson (1949) collected by inventory crews was reasonably accurate (Drummond estimated that 3–11% of the black spruce type in the Big Falls 1978).