Forest Insect & Disease Leaflet 60
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
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. -
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 -
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). -
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. -
Pseudotsuga- Tsuga Forest
Spatial Relationship of Biomass and Species Distribution in an Old-Growth Pseudotsuga- Tsuga Forest Jiquan Chen, Bo Song, Mark Rudnicki, Melinda Moeur, Ken Bible, Malcolm North, Dave C. Shaw, Jerry F. Franklin, and Dave M. Braun ABSTRACT. Old-growth forests are known for their complex and variable structure and function. In a 12-ha plot (300 m x 400 m) of an old-growth Douglas-fir forest within the T. T. Munger Research Natural Area in southern Washington, we mapped and recorded live/dead condition, species, and diameter at breast height to address the following objectives: (1) to quantify the contribution of overstory species to various elements of aboveground biomass (AGB), density, and basal area, (2) to detect and delineate spatial patchiness of AGB using geostatisitcs, and (3) to explore spatial relationships between AGB patch patterns and forest structure and composition. Published biometric equations for the coniferous biome of the region were applied to compute AGB and its components of each individual stem. A program was developed to randomly locate 500 circular plots within the 12-ha plot that sampled the average biomass component of interest on a per hectare basis so that the discrete point patterns of trees were statistically transformed to continuous variables. The forest structure and composition of low, mediate, and high biomass patches were then analyzed. Biomass distribution of the six major'species across the stand were clearly different and scale- dependent. The average patch size of the AGB based on semivariance analysis for Tsuga heterophy/la, Abies amabi/is, A. grandis, Pseudotsuga menziesii, Thuja plicata, and Taxus brevifolia were 57.3, 81.7, 37, 114.6, 38.7, and 51.8 m, respectively. -
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. -
Hybridization of the California Firs
Forest Science, Vol. 34, No. I, pp. 139-151. Copyright 1988 by the Society of American Foresters Hybridization of the California Firs William B. Critchfield Abstract. Four groups of firs (sections, in the most recent classification of Abies) are represented in California. Crossing within these sections is possible and even easy, and in two of the sections intergrading populations between highly crossable taxa are wide spread in California. An exception is A. amabilis, a Northwestern fir that has not been crossed with other species in the same section {Grandes: A. concolor, A. grandis) or in other sections (e.g., Nobiles: A magnified). Crossing species in different sections is usually difficult or impossible. The genetic isolation of A. bracteata, an endemic species classified as a monotypic subgenus or section, may be nearly complete: two probable hybrids with A. concolor died at a few years of age. A few putative hybrids from inter- sectional crosses between species in Grandes and Nobiles died within months of germi nation. Intersectional crosses with firs outside California (two Mexican and four Eur asian species) all failed except A. concolor x A. religiosa, which produced numerous healthy hybrids. The common occurrence of genetic barriers in Abies is at odds with the long-held view that it is easy to hybridize fir species. For. Sci. 34(1): 139-151. Additional key words. Abies, interspecific hybrids, crossability, classification. The ability of species to hybridize has not been explored as systemati cally in the genus Abies (true firs) as it has in other genera of Pinaceae such as Pinus and Pice a. -
Botanist Interior 43.1
2005 THE MICHIGAN BOTANIST 109 THE BIG TREES AND SHRUBS OF MICHIGAN 46. Pseudotsuga menziesii (Mirbel) Franco Douglas-fir Elwood B. Ehrle Department of Biological Sciences Western Michigan University Kalamazoo, MI 49008 [email protected] The largest known Douglas-fir tree in Michigan is located on the North Cam- pus of the University of Michigan in Ann Arbor, MI, in Washtenaw County in the southeastern part of Michigan’s Lower Peninsula. Description of the Species: The Douglas-fir is an evergreen tree with a usu- ally straight trunk and conical crown. The soft, flexible leaves are 2–2.5 cm long, somewhat 2-ranked, and have constricted bases. The branchlets are mostly smooth and exhibit oval scars where leaves have been removed. The cones have conspicuous three-lobed bracts extending beyond the cone scales, with the mid- dle lobe long and narrow. This species is native to the Rocky Mountains and the North American Pacific Northwest coast, where it forms extensive forests of large trees. It is an important lumber tree in the northwest. In Michigan, it is fre- quently planted as a park or lawn tree and is grown as a Christmas tree which holds its needles better than Balsam Firs or Spruces. The common name honors David Douglas, 1799–1834. Location of Michigan’s Big Tree: The North Campus of the University of Michigan is located on the north side of Ann Arbor, MI. It can be reached by tak- ing exit 180 off of I-94 and going north on Rt. 23 through Ann Arbor to Ply- mouth Road (exit 41). -
Insects That Feed on Trees and Shrubs
INSECTS THAT FEED ON COLORADO TREES AND SHRUBS1 Whitney Cranshaw David Leatherman Boris Kondratieff Bulletin 506A TABLE OF CONTENTS DEFOLIATORS .................................................... 8 Leaf Feeding Caterpillars .............................................. 8 Cecropia Moth ................................................ 8 Polyphemus Moth ............................................. 9 Nevada Buck Moth ............................................. 9 Pandora Moth ............................................... 10 Io Moth .................................................... 10 Fall Webworm ............................................... 11 Tiger Moth ................................................. 12 American Dagger Moth ......................................... 13 Redhumped Caterpillar ......................................... 13 Achemon Sphinx ............................................. 14 Table 1. Common sphinx moths of Colorado .......................... 14 Douglas-fir Tussock Moth ....................................... 15 1. Whitney Cranshaw, Colorado State University Cooperative Extension etnomologist and associate professor, entomology; David Leatherman, entomologist, Colorado State Forest Service; Boris Kondratieff, associate professor, entomology. 8/93. ©Colorado State University Cooperative Extension. 1994. For more information, contact your county Cooperative Extension office. Issued in furtherance of Cooperative Extension work, Acts of May 8 and June 30, 1914, in cooperation with the U.S. Department of Agriculture, -
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.