Spruces, Firs and Larches 1449 Established Using Genetically Modified P
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Common Name Scientific Name Comments Evergreen Trees
Common Name Scientific Name Height* Spread Native Fall Color Ornamental Bark Flowering Wind Tolerant Tolerant Salt Well Drained Soil Moist Soil Full Sun Partial Sun Shade Comments Evergreen Trees Austrian Pine Pinus nigra 60' 30' x x x Vigerous, dark green needles (Behind Brenner's Castle Hill parking lot) Blue Spruce Picea pungens 60 30 x x Slow growing, bluish tint to needles English Laurel Prunus laurocerasus 10' 15' x x x x x x Good hedge.Dark green waxy leaves. (Corner Observatory & Seward St) Holly Ilex species 10' 10' x x Beautiful foliage and berries. Need male & female (City Hall west side) Lodgepole Pine (Bull Pine) Pinus contorta 35' 35' x x x x x x Fast growing, good for containers, screening (Crescent Park by picnic shelters) Mountain Hemlock Tsuga mertensiana 30' 15' x x x x x x x x Good for slopes, rock gardens, containers. Slow growing. (Wells Fargo parking lot) Sitka Spruce Picea sitchensis 100' 50' x x x x x Prone to aphids. Prolific, native of SE Alaska Western Hemlock Tsuga heterophylla 100 50 x x x x x x Fast growing. Can be pruned into a hedge (SJ Campus -Jeff Davis St.) Western Red Cedar Thuja plicata 80' 40' x x Beautiful foliage. Interesting bark. Subalpine Fir Abies lasiocarpa 100' 20' x Beautiful conical form. (Two across from Market Center parking lot.) Noble Fir Abies procera 100' 30' x Dark green, fast growing, beautiful large specimens at 1111 HPR Siberian Spruce Picea Omorika 20' 4' x x x Blue-green foliage. 'Bruns' at Moller Field, 'Weeping Brun's' at BIHA office Japanese White Pine Pinus parviflora 6' 3' x x Negishi' at Moller Field with blue-green foliage Korean Fir Abies koreana 15' 10' x x Horstmann's silberlocke' at Moller Field; silver foliage Western White Pine Pinus monticola 60' 20' x x x Fast growing, conical form (Fine Arts Camp Rasmusen Center, Lake St. -
Eastern Deciduous Forest
Eastern Deciduous Forest Physical description Most of the terrain is rolling except for the Ozark Mountains, which can be steep. The average annual precipitation ranges from approximately 35 inches to 90 inches and is usually well-distributed throughout the year. Summers are hot; winters are cold. Dominant vegetation Deciduous trees dominate the landscape across the Eastern Deciduous Forest ecoregion where there is a lack of disturbance. Depending on location, trees such as oaks, hickories, maples, American beech, basswood, buckeye, yellow poplar, walnut, and birches are common in the overstory and can be indicators of a climax successional stage. Prevalent midstory trees include flowering dogwood, sassafras, sourwood, eastern redbud, hophornbeam, American hornbeam, and striped maple. Common shrubs include arrowwood, black huckleberry, blueberries, hawthorn, pawpaw, spicebush, viburnums, and witchhazel. A wide variety of forbs and ferns may be found in the understory. Common evergreen trees on many sites undergoing succession include eastern redcedar and shortleaf pine. Figure 2. Deciduous forest cover occurs over the Eastern Deciduous Forest ecoregion, except where areas have been cleared for agriculture and livestock. Changes in the composition, structure and function of the Eastern Deciduous Forest have already occurred during the past 100 years with the loss of American chestnut and the near total exclusion of fire. Prior to fire suppression, savannas and woodlands dominated by oak and shortleaf pine were prevalent over much of this ecoregion. Well-interspersed with forested areas in the Eastern Deciduous Forest ecoregion are agricultural fields, pastures and hayfields, and fields undergoing succession. Virtually all of these “old- fields” have been cropped in the past, and the vast majority has since been planted to nonnative grasses, especially tall fescue. -
EVERGREEN TREES for NEBRASKA Justin Evertson & Bob Henrickson
THE NEBRASKA STATEWIDE ARBORETUM PRESENTS EVERGREEN TREES FOR NEBRASKA Justin Evertson & Bob Henrickson. For more plant information, visit plantnebraska.org or retreenbraska.unl.edu Throughout much of the Great Plains, just a handful of species make up the majority of evergreens being planted. This makes them extremely vulnerable to challenges brought on by insects, extremes of weather, and diseases. Utilizing a variety of evergreen species results in a more diverse and resilient landscape that is more likely to survive whatever challenges come along. Geographic Adaptability: An E indicates plants suitable primarily to the Eastern half of the state while a W indicates plants that prefer the more arid environment of western Nebraska. All others are considered to be adaptable to most of Nebraska. Size Range: Expected average mature height x spread for Nebraska. Common & Proven Evergreen Trees 1. Arborvitae, Eastern ‐ Thuja occidentalis (E; narrow habit; vertically layered foliage; can be prone to ice storm damage; 20‐25’x 5‐15’; cultivars include ‘Techny’ and ‘Hetz Wintergreen’) 2. Arborvitae, Western ‐ Thuja plicata (E; similar to eastern Arborvitae but not as hardy; 25‐40’x 10‐20; ‘Green Giant’ is a common, fast growing hybrid growing to 60’ tall) 3. Douglasfir (Rocky Mountain) ‐ Pseudotsuga menziesii var. glauca (soft blue‐green needles; cones have distinctive turkey‐foot bract; graceful habit; avoid open sites; 50’x 30’) 4. Fir, Balsam ‐ Abies balsamea (E; narrow habit; balsam fragrance; avoid open, windswept sites; 45’x 20’) 5. Fir, Canaan ‐ Abies balsamea var. phanerolepis (E; similar to balsam fir; common Christmas tree; becoming popular as a landscape tree; very graceful; 45’x 20’) 6. -
Review of British Columbia's Contemporary and Projected
Review of British Columbia’s contemporary and projected western larch seed planning zones in light of climate change. Barry Jaquish Research and Knowledge Management Branch, B.C. Ministry of Forests and Range Kalamalka Forestry Centre, Vernon, B.C. February 26, 2010 Background The catastrophic effects of mountain pine beetle on the forests of central British Columbia combined with the projected effects of climate change have stimulated intense debate over forest management throughout the region. One commonly suggested approach to mitigating these effects is to increase the region’s ecosystem complexity through the planting of either exotic tree species or native species whose distribution lies outside the central Interior. While the benefits of introducing exotic species remains controversial and speculative, the assisted, or facilitated, migration of native species presents a valuable tool for enhancing ecological complexity and ensuring the species’ pace of migration matches the expected rate of climate change. Western larch (Larix occidentalis Nutt), a species native to the upper Columbia River basin in southeastern B.C. (Fig. 1), is often suggested as a desirable candidate for introduction because of its rapid early growth, desirable wood properties, and generalist mode of adaptation. Indeed, western larch is already commonly planted north of its native range in southeastern B.C. (Plate 1) and over the last three decades numerous small operational and research plantings have demonstrated western larch’s reforestation potential on many sites throughout the central Interior (Plates 2, 3, 4, and 5). Ecologically, it appears that western larch’s fundamental niche exceeds its realized niche. Climate envelope modelling also suggests that the future climate space amenable to western larch lies far north of its contemporary distribution. -
Resistance to Low and Negative Temperatures of Rhododendrons (Rhododendron) in the Botanical Garden of Šiauliai University in 2
Available online at www.notulaebotanicae.ro Print ISSN 0255-965X; Electronic ISSN 1842-4309 Not. Bot. Hort. Agrobot. Cluj 36 (1) 2008, 59-62 Notulae Botanicae Horti Agrobotanici Cluj-Napoca Resistance to Low and Negative Temperatures of Rhododendrons (Rhododendron) in the Botanical Garden of Šiauliai University in 2002-2007 Aurelija MALCIŪTĖ1) , Jonas Remigijus NAUJALIS2) , Antanas SVIRSKIS3) 1) Šiauliai University, Botanical Garden, Paitaičių Str. 4, LT-76284, Šiauliai, Lithuania, e-mail: [email protected] 2) Vilnius University, Faculty of Natural Sciences, Department of Botany and Genetics, M. K.Čiurlionio Str. 21/27, LT-03101, Vilnius, e-mail: [email protected] 3) Šiauliai University, Instituto 1, 58344 Akademija, Kėdainių distr., Lithuania, e-mail: [email protected] Abstract Rhododendrons are not native to Lithuania, but are often cultivated in botanical gardens, various public and private green plantations. Resistance to low temperatures are among the most important criteria in evaluating the condition of the rhododendron collection in the Botanical Garden of ŠU. The research initiated in the ŠU Botanical Garden will help in the selection and propagation of ornamental and tolerant to low temperatures representatives of species and cultivars, suitable for cultivation in northern Lithuania. Keywords: rhododendron, low temperature, ŠU Botanical Garden Introduction research on the plants of the Rhododendron genus in the region of Žemaitija uplands has been performed yet. Introduction of plants is one of the most important tasks of Botanical Garden of Šiauliai University (further Materials and methods referred as ŠU) which constantly expands the assortment of woody plants and that is the reason for the beginning Resistance to low temperatures are among the most of introduction of the Rhododendrons (Rhododendron L.) important criterion evaluated condition of rhododendrons genus plants. -
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 -
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. -
Fall Color Is a Byproduct of the Physiological Response of Temperate-Zone Plants to Shortening Days
Printed in: Southwest Horticulture (2001) 18(6):6 The Colors of Fall Ursula Schuch, Plant Sciences Department, University of Arizona, Tucson Cool nights and warm, sunny days signal the onset of fall, and perfect weather for the development of brilliant crimson, gold, copper or yellow foliage. Fall color is a byproduct of the physiological response of temperate-zone plants to shortening days. Best fall colors are generally seen in deciduous, broadleaf woody plants that originate in USDA zones 3 to 9. In Arizona, fall color is scarce in the low desert, but is displayed more generously at higher elevations. Chlorophyll is responsible for the green color of leaves or stems and enables plants to produce sugars through the process of photosynthesis. In green leaves, chlorophyll is the dominant pigment. Visible light is absorbed by pigments, and leaves appear green because chlorophyll absorbs red and blue light while transmitting and reflecting green light. Carotenoids are accessory pigments in the photosynthesis process with colors in shades of yellow to orange; however, they are much less abundant than chlorophyll. Starting in spring, when plant growth begins for temperate-zone plants, and throughout summer, chlorophyll is continuously produced in the growing leaves to enable maximum food production. This is the time of greatest stem elongation, new leaf production, and growth in girth. As summer transitions into fall, plants respond to shorter days with reduced stem elongation, initiation of leaf abscission, reduced chlorophyll production, and increased production of other pigments. This marks the onset of dormancy and the beginning of frost hardiness. The splendor of fall color begins when chlorophyll production declines in the leaves and when the less abundant carotenoids unveil yellow to orange hues, or anthocyanins flaunt colors of red and purple. -
Modeling the Effects of Climate Change on Western Larch Stands in Idaho Eric Olson Advisor: Kristen M
Northern Arizona University School of Forestry Spring 2018 Modeling the Effects of Climate Change on Western Larch Stands in Idaho Eric Olson Advisor: Kristen M. Waring, Ph. D. Readers: Peter Fulé, Ph. D. and John Riling TABLE OF CONTENTS Abstract Section 2.6. Management Strategy Modeling Section 1. Introduction Forest Vegetation Simulator Time Scale Section 1.1. Climate Change Section 1.2. Land Management and Western Larch Climate-FVS USFS National Forests Climate-FVS Regeneration Western Larch Fire and Fuel Extension Study Approach Section 3. Results Section 2. Methods Section 3.1 Current Conditions at Project Scale Section 2.1. Study Areas Section 3.2 Future Projections Section 2.2. Data Sources BNF Section 2.3. Treatments Defined No Action Section 2.4. Desired Landscape-Scale Conditions Resistance Species Composition Resilience Density IPNF Fire Hazard No Action Section 2.5. Management Options Resistance No Action Resilience Resistance Resilience Section 4. Discussion Section 5. Conclusion Literature Cited 1 Abstract Climate change research has shown irrefutably that global temperatures are rising, and almost all climate-model projections agree that in the coming decades the western US is likely to experience warmer springs and summers. Hotter and drier conditions are a concern for the future of western forests because climate is an important factor in determining plant distributions. The general effects of climate change on forests include a significant increase to the variability in disturbance regimes, shifts in species ranges, or a shift in germination and establishment requirements. Adding to the complexity of challenges faced by western forests are the poor land management practices of the 20th century, such as fire suppression and high- grade logging, which have led to an adverse change in forest structure including a decline in shade intolerant species such as western larch (Larix occidentalis). -
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.