Hybridization of the California Firs
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Tree Species Distribution Maps for Central Oregon
APPENDIX 7: TREE SPECIES DISTRIBUTION MAPS FOR CENTRAL OREGON A7-150 Appendix 7: Tree Species Distribution Maps Table A7-5. List of distribution maps for tree species of central Oregon. The species distribution maps are prefaced by four maps (pages A7-151 through A7-154) showing all locations surveyed in each of the four major data sources Map Page Forest Inventory and Analysis plot locations A7-151 Ecology core Dataset plot locations A7-152 Current Vegetation Survey plot locations A7-153 Burke Museum Herbarium and Oregon Flora Project sample locations A7-154 Scientific name Common name Symbol Abies amabilis Pacific silver fir ABAM A7-155 Abies grandis - Abies concolor Grand fir - white fir complex ABGR-ABCO A7-156 Abies lasiocarpa Subalpine fir ABLA A7-157 Abies procera - A. x shastensis Noble fir - Shasta red fir complex ABPR-ABSH A7-158 [magnifica x procera] Acer glabrum var. douglasii Douglas maple ACGLD4 A7-159 Alnus rubra Red alder ALRU2 A7-160 Calocedrus decurrens Incense-cedar CADE27 A7-161 Chrysolepis chrysophylla Golden chinquapin CHCH7 A7-162 Frangula purshiana Cascara FRPU7 A7-163 Juniperus occidentalis Western juniper JUOC A7-164 Larix occidentalis Western larch LAOC A7-165 Picea engelmannii Engelmann spruce PIEN A7-166 Pinus albicaulis Whitebark pine PIAL A7-167 Pinus contorta var. murrayana Sierra lodgepole pine PICOM A7-168 Pinus lambertiana Sugar pine PILA A7-169 Pinus monticola Western white pine PIMO3 A7-170 Pinus ponderosa Ponderosa pine PIPO A7-171 Populus balsamifera ssp. trichocarpa Black cottonwood POBAT A7-172 -
Natural Regeneration of White and Red Fir. . . Influence of Several Factors. Berkeley, Calif., Pacific SW
PACIFIC SOUTHWEST Forest and Range FOREST SERVICE. U. S. DEPARTMENT OF AGRICULTURE P.O. BOX 245, BERKELEY, CALIFORNIA 94701 Experiment Station U.S.D.A. FOREST SERVICE RESEARCH PAPER PSW- 58 /1970 Gordon, Donald T. 1970. Natural regeneration of white and red fir. influence of several factors. Berkeley, Calif., Pacific SW. Forest & Range Exp. Sta. 32 p., illus. (U.S.D.A. Forest Serv. Res. Pap. PSW-58) In a group of studies at Swain Mountain Experimental Forest in northeastern California, seedling survival and mortality were analyzed within the general framework of seed production and dispersal, germination, seedbed condition, soil surface temperature, insolation, soil moisture, and vegetative competition. Factors found to favor seedling establishment were abundance of sound seed, mineral soil seedbed, and probably some shade in the first year. Chief obstacles to seedling survival and growth included strong insolation, deep litter, insects, competing low vegetation, and time between good seed years. The most practical approach to securing natural regeneration appears to be keeping abundant seed trees close to a prepared mineral soil seedbed. Oxford: 231–181.525[+ 174.7 Abies concolor + 174.7 Abies magnifica + 174.7 Abies magnifica var. shastensis]. Retrieval Terms: Abies concolor; Abies magnifica; Abies magnifica var. shastensis; natural regeneration; seedling establishment; seedbed; protective shading; seed production; seedling mortality; Swain Mountain Experimental Forest. Gordon, Donald T. 1970. Natural regeneration of white and red fir. influence of several factors. Berkeley, Calif., Pacific SW. Forest & Range Exp. Sta. 32 p., illus. (U.S.D.A. Forest Serv. Res. Pap. PSW-58) In a group of studies at Swain Mountain Experimental Forest in northeastern California, seedling survival and mortality were analyzed within the general framework of seed production and dispersal, germination, seedbed condition, soil surface temperature, insolation, soil moisture, and vegetative competition. -
Balsam Woolly Adelgid
A New Utah Forest Insect This fact sheet Pest: Balsam Woolly Adelgid introduces an invasive forest pest, the balsam By: Darren McAvoy, Extension Forestry Assistant Professor, woolly adelgid, and Diane Alston, Professor & Extension Entomologist, discusses its impacts on Ryan Davis, Arthropod Diagnostician, Utah forests, life cycle Megan Dettenmaier, Extension Forestry Educator traits, identifying characteristics, control Introduction methods, and steps that In 2017, the USDA Forest Service’s Forest Health Protection (FHP) group in Utah partners are taking Ogden, Utah detected and confirmed the presence of a new invasive forest to combat this pest. pest in Utah called the balsam woolly adelgid (BWA). First noticed in the mountains above Farmington Canyon and near Powder Mountain Resort, it has Dieback and decline of subalpine fir due to attack by balsam woolly adelgid. Photo credit: Darren McAvoy. 2017, forest health professionals visited Farmington Canyon on the ground and found branch node swelling (a node is where branch structures come together) and old deposits of woolly material on mature subalpine fir trees. Suspected to have originated in the Caucasus Mountains between Europe and Asia, BWA was first detected in North America in Maine, in 1908, and in California about 20 years later. It was detected in Idaho near Coeur d’Alene in 1983 and has since spread across northern Idaho. It is believed that separate invasions of subspecies or races of BWA may differentially impact tree host species. Dieback of subalpine fir, pacific silver (Abies amabilis) and grand fir (A. grandis) in Idaho is widespread. In the western Payette National Forest, north of Boise, an estimated 70% of subalpine fir trees are dead and falling down. -
Seed Maturity in White Fir and Red Fir. Pacific Southwest Forest and Range Exp
PACIFIC SOUTHWEST Forest and Range FOREST SERVICE U. S. DEPARTMENT OF AGRICULTURE P.O. BOX 245, BERKELEY, CALIFORNIA 94701 Experiment Station USDA FOREST SERVICE RESEARCH PAPER PSW-99 /1974 CONTENTS Page Summary ................................................... 1 Introduction ................................................. 3 Methods .................................................... 3 Testing Fresh Seeds ....................................... 3 Testing Stratified Seeds .................................... 3 Seedling Vigor Tests ...................................... 4 Artificial Ripening Trial ................................... 4 Other Observations ........................................ 4 Results and Discussion ....................................... 5 Cone Specific Gravity ..................................... 5 Seed Germination, byCollection Date ....................... 5 Seed GerminationandCone Specific Gravity ................ 7 Red Fir Seedling Vigor .................................... 9 ArtificialRipening of White Fir Seeds ....................... 9 OtherMaturity Indices ..................................... 9 Application ................................................. 10 Literature Cited.............................................. 12 THE AUTHOR WILLIAM W. OLIVER is doing silvicultural research on Sierra Nevada conifer types with headquarters at Redding, California. He earned a B.S. degree (1956) in forestry from the University of New Hampshire, and an M.F. degree (1960) from the University of Michigan. A native of -
Bridgeoporus Nobilissimus Is Much More Abundant Than Indicated by the Presence of Basidiocarps in Forest Stands
North American Fungi Volume 10, Number 3, Pages 1-28 Published May 29, 2015 Bridgeoporus nobilissimus is much more abundant than indicated by the presence of basidiocarps in forest stands Matthew Gordon1 and Kelli Van Norman2 1Molecular Solutions LLC, 715 NW Hoyt St., #2546, Portland, OR 97208, USA 2Interagency Special Status/Sensitive Species Program, USDI Bureau of Land Management Oregon State Office & USDA Forest Service Region 6, 1220 SW 3rd Ave., Portland, OR 97204, USA Gordon, M., and K. Van Norman. 2015. Bridgeoporus nobilissimus is much more abundant than indicated by the presence of basidiocarps in forest stands. North American Fungi 10(3): 1-28. http://dx.doi:10.2509/naf2015.010.003 Corresponding author: Matt Gordon [email protected]. Accepted for publication May 4, 2015. http://pnwfungi.org Copyright © 2015 Pacific Northwest Fungi Project. All rights reserved. Abstract: The polypore Bridgeoporus nobilissimus produces large perennial basidiocarps on large diameter Abies stumps, snags and trees in coniferous forests of the Pacific Northwest. Despite the size and persistence of the basidiocarps, they are rarely observed, making the conservation of this species a concern. We determined that a genetic marker for this fungus could be detected in DNA extracted from wood cores taken from trees hosting basidiocarps. We then tested 105 trees and stumps that did not host B. nobilissimus basidiocarps in plots surrounding B. nobilissimus conks, and 291 trees and stumps in randomly located plots in four stands that contained at least one B. nobilissimus basidiocarp. We found that trees of all sizes throughout all of the stands hosted B. -
CHRISTMAS TREES FACTSHEET November 2008 an INTRODUCTION Ref: 050403
CALU CHRISTMAS TREES FACTSHEET November 2008 AN INTRODUCTION Ref: 050403: INTRODUCTION Growing Christmas trees is an option which more and more garden centres, nurseries and other businesses are considering. Over recent years production numbers have increased significantly: from 4.4m trees produced in the UK in 2001, to 6.5m in 2005. Nevertheless, approximately one million Christmas trees are imported from the continent, mainly Denmark, each year. There are good arguments for setting up a Christmas tree plantation, including the strength of the Euro. This is making imported trees look less attractive as they become relatively more expensive. Home grown Christmas trees also have an attractive marketing factor which can encourage customers to buy them. However, setting up and running a Christmas tree plantation is a time and labour intensive operation which requires skills as well as foresight: it will take around seven to 10 years before the first crop of Christmas trees will be ready for the market. SPECIES Many species are used as Christmas trees: some are more fashionable in some years than others. Historically, it was the Norway spruce that was the traditional Christmas tree. In recent years various types of fir tree have overtaken the spruce in terms of popularity. This is because they tend to hold their needles better and are less prickly. However, they are slower growing and therefore more expensive to produce. Table 1 provides an overview of the characteristics of the most commonly bought Christmas tree species in the UK: Table 1: Common Christmas tree species Common Botanical name Characteristics name Noble fir Abies procera Typical “Christmassy” scent, soft needles, approx. -
Plant Data Sheet Abies Procera Noble
Firefox http://depts.washington.edu/propplnt/Plants/abies procera.htm Plant Data Sheet Abies procera noble fir Range Mountains of Northwest Oregon and Southwest Washington between latitude 44N and 48N. Climate, elevation Moist maritime climate. Cool temperatures, high precipitation. Annual precipitation 1960-2410 mm. Three quarters of precipitation falls between October and March as snow. Mid to upper elevations. Local occurrence (where, how common) West slopes of the Cascade Mountains. Habitat preferences Prefers moist deep cool well-drained soil. However, can grow on a wide variety of soils including rocky if there is enough moisture. Takes sun to part shade. Does not tolerate high wind or soil with high pH. Plant strategy type/successional stage (stress-tolerator, competitor, weedy/colonizer, seral, late successional) Associated species Associates with most Northwest confers throughout the range, Alaska huckleberry, red huckleberry, Cascades azalea, Pacific rhododendron, bear grass, fawn lily, inside-out-flower. May be collected as: (seed, layered, divisions, etc.) Seed Collection restrictions or guidelines Seeds are dispersed in September - October. Noble fir starts to produce seed around 50 years of age. Time between good cone crops could be up to 6 years. Seed quality is poor. Good seed quality usually correlates with good cone crops. 1 of 2 2/11/2021, 6:33 PM Firefox http://depts.washington.edu/propplnt/Plants/abies procera.htm Seed germination (needs dormancy breaking?) Seed life (can be stored, short shelf-life, long shelf-life) Recommended seed storage conditions Propagation recommendations (plant seeds, vegetative parts, cuttings, etc.) Soil or medium requirements (inoculum necessary?) Installation form (form, potential for successful outcomes, cost) Recommended planting density Care requirements after installed (water weekly, water once etc.) Normal rate of growth or spread; lifespan In landscape settings grows to 50-100 feet tall. -
Giant Sequoia Insect, Disease, and Ecosystem Interactions1
Giant Sequoia Insect, Disease, and Ecosystem Interactions1 Douglas D. Piirto2 Abstract: Individual trees of giant sequoia (Sequoia gigantea [Lindl.] afflict and kill other trees." Similarly Hartesveldt (1962) Decne.) have demonstrated a capacity to attain both a long life and very concurred that "Sequoia's longevity and great size have large size. It is not uncommon to find old-growth giant sequoia trees in their native range that are 1,500 years old and over 15 feet in diameter at been attributed by nearly all writers, popular and scientific, breast height. The ability of individual giant sequoia trees to survive over to its few insect and fungus parasites and the remarkable such long periods of time has often been attributed to the species high resistance of the older trees to damage or death by fire. resistance to disease, insect, and fire damage. Such a statement, however, is There is no record of an individual sequoia living in its a gross oversimplification, given broader ecosystem and temporal interac- tions. For example, why isn't there a greater representation of young-growth natural range as having been killed by either fungus or insect giant sequoia trees throughout the mixed-conifer belt of the Sierra Nevadas? attack." Even as recently as 1991 Harlow and others (1991) What other factors, in addition to physical site characteristics, limit giant stated: "Insects and fungi cause but minor damage, and no sequoia to its present range and grove boundaries? How does fire and fire large Bigtree killed by them has ever been found." frequency affect disease and insect interrelationships in the giant sequoia/ mixed-conifer ecosystem? Are current forest management strategies (e.g., It is finally being recognized that giant sequoia is fire suppression, prescribed burning programs) affecting these interactions? subject to the same natural forces as other tree species (Bega Giant sequoia trees are subject to the same natural forces (e.g., insect and 1964, Harvey and others 1980, Parmeter 1987, Piirto 1977, disease organisms) as other tree species. -
Survival of Live Christmas Trees Profile: Nordmann Fir This Pot-In-Pot Nursery in Denmark Produces 90,000 to 100,000 Showing the Flag
volume 2 | number 4 fall 2007 survival of live christmas trees profile: nordmann fir This Pot-in-Pot nursery in Denmark produces 90,000 to 100,000 Showing the flag. Nordmann fir are marketed in Europe under container-grown Nordmann fir each year. the “Original Nordmann” label. Christmas Tree Species Profile: Nordmann fir Abies nordmanniana By: Bert Cregg, Ph.D. Michigan State University, Department of Horticulture and Department of Forestry Photos by Rick Bates, Ph.D. Pennsylvania State University, Department of Horticulture One of the great things about working with Christmas trees is that we get to work with some beautiful and fascinating plants. Over the years, many species of pines, spruces, firs, and even cedars have been used as Christmas trees. Each species has its unique appeal and every species has a story. Beginning with this issue of the Great Lake Christmas Tree Journal, I will present profiles of interesting Christmas tree species used in the Great Lakes region and elsewhere. I’ll discuss the basic biology and ecology of the species, highlight some of the advantages or concerns of the species for Christmas tree production, and throw in a little trivia or other titillating tidbits. Nordmann fir Abies nordmanniana not given to feint praise, calls Nordmann popularity of this species is due to sever- Beauty, as they say, is in the eye of the fir,“stately, elegant, perhaps the hand- al factors. First and foremost are the beholder, but few can argue that somest of the firs.” Nordmann fir is by far glossy, dark green needles, which are Nordmann fir is among the most beauti- the most popular Christmas tree species darker than almost any fir except for ful conifers found anywhere. -
Curtis/True Fir-Hemlock Trials
United States Department of Agriculture True Fir-Hemlock Forest Service Pacific Northwest Spacing Trials: Research Station General Design and First Results Technical Report PNW-GTR-492 May 2000 Robert O. Curtis, Gary W. Clendenen and Jan A. Henderson Authors Robert O. Curtis is an emeritus scientist and Gary W. Clendenen is a forester, Pacific Northwest Research Station, 3625-93d Ave. SW, Olympia, WA 98512-9193; and Jan A. Henderson is an area ecologist, Mount Baker-Snoqualmie National Forest, 21905-64th Ave. West, Mountlake Terrace, WA 98043. Abstract Curtis, Robert O.; Clendenen, Gary W.; Henderson, Jan A. 2000. True fir-hemlock spacing trials: design and first results. Gen. Tech. Rep. PNW-GTR-492. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 35 p. A series of 18 precommercial thinning trials was established in true fir-hemlock stands in the Olympic Mountains and along the west side of the Cascade Range in Washington and Oregon from 1987 through 1994. This paper documents estab- lishment of these installations and presents some preliminary observations and results. Substantial differences in growth rates in height and diameter were ob- served among Pacific silver fir, western hemlock, and noble fir. Diameter growth of all species increased as spacing increased, but height growth of silver fir and noble fir decreased at wider spacings in some areas. These installations will pro- vide a unique source of information on early development of managed stands of these species, for which little information now is available. Keywords: Abies, spacing, precommercial thinning, true firs. This page left blank intentionally. -
Fire History of Pseudotsuga Menziesii and Abies Grandis Stands in The
Fire History of Pseudotsuga men:iesii and Abies grandis Stands in the Blue Mountains of Oregon and Washington by Kathleen Ryoko Maruoka This report is submitted in partial satisfaction of Supplemental Cooperative Agreement # PNW 92-0179 between the USDA Forest Service and the University of Washington. It was submitted as a M.S. thesis at the University of Washington. March 11, 1994 Fire History of Pseudotsuga menziesii and Abies grandis Stands in the Blue Mountains of Oregon and Washington by Kathleen Ryoko Maruoka A thesis submitted in partial fulfillment of the requirements for the degree of Master of Science University of Washington 1994 Approved by (C an of Supervib6ry Committee) A&VZ,Ce Ck/ ge1-64411) Program Authorized to Offer Degree 1-77`e s r Date Master's Thesis In presenting this thesis in partial fulfillment of the requirements for a Master's degree at the University of Washington, I agree that the Library shall make its copies freely available for inspection. I further agree that extensive copying of this thesis is allowable only for scholarly purposes. consistent with "fair use" as prescribed in the U.S. Copyright Law. Any other reproduction for any purposes or by any means shall not be allowed without my written . permission. Signature Date I , University of Washington Abstract A Fire History Survey in Selected Pseudotsuga men:testi and Abies grandis Stands in the Blue Mountains of Oregon and Washington by Kathleen Ryoko Maruoka Chairman of Supervisory Committee: Professor James K. Agee College of Forest Resources Fifteen sites in the Blue Mountains of Oregon and Washington were sampled to survey fire frequency in stands ranging from Pseudotsuga menziesii associations to dry Abies grandis associations. -
Local Variation in Intergrading Abies Grandis—Abies Concolor Populations in the Central Oregon Cascades: Needle Morphology and Periderm Color
BOT. GAZ. 134(3):209-220. 1973. LOCAL VARIATION IN INTERGRADING ABIES GRANDIS—ABIES CONCOLOR POPULATIONS IN THE CENTRAL OREGON CASCADES: NEEDLE MORPHOLOGY AND PERIDERM COLOR DONALD B. ZOBEL Department of Botany and Plant Pathology, Oregon State University, Corvallis, Oregon 97331 ABSTRACT In the central Oregon Cascades, grand fir morphology varies from that of typical Abies grandis to that of populations with a variety of morphological types, some closely resembling A. concolor. Low- elevation populations west of the Cascade crest, mostly on river terraces, resemble A. grandis. High- elevation west-side populations, disjunct from those at low elevations and occupying ridge tops and steep, dry slopes, include trees with some traits of A. concolor. Populations on the east flank of the Cascades show a greater but widely variable influence of A. concolor. East-side populations vary locally with aspect, being most like A. grandis on north slopes, but they do not clearly vary with elevation. Incidence of characteristics resembling A. concolor increases from north to south within the study area, although this pattern shows deviations not associated with obvious changes in topography. Periderm color and needle morphology show the same general relationships between the populations sampled. Either "maxi- mum number of adaxial stomatal rows" or "percentage of length of needle with adaxial stomata" can be used to describe the extent of adaxial stomata. Needle notch depth is not consistently correlated with stomata( characteristics on a tree-to-tree basis, but shows a similar, less distinct, geographic and habitat pattern. The variation within populations is greater in the intermediate populations than in those of "typical" A.