Understanding Names of Oregon Trees
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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 -
Western Juniper Woodlands of the Pacific Northwest
Western Juniper Woodlands (of the Pacific Northwest) Science Assessment October 6, 1994 Lee E. Eddleman Professor, Rangeland Resources Oregon State University Corvallis, Oregon Patricia M. Miller Assistant Professor Courtesy Rangeland Resources Oregon State University Corvallis, Oregon Richard F. Miller Professor, Rangeland Resources Eastern Oregon Agricultural Research Center Burns, Oregon Patricia L. Dysart Graduate Research Assistant Rangeland Resources Oregon State University Corvallis, Oregon TABLE OF CONTENTS Page EXECUTIVE SUMMARY ........................................... i WESTERN JUNIPER (Juniperus occidentalis Hook. ssp. occidentalis) WOODLANDS. ................................................. 1 Introduction ................................................ 1 Current Status.............................................. 2 Distribution of Western Juniper............................ 2 Holocene Changes in Western Juniper Woodlands ................. 4 Introduction ........................................... 4 Prehistoric Expansion of Juniper .......................... 4 Historic Expansion of Juniper ............................. 6 Conclusions .......................................... 9 Biology of Western Juniper.................................... 11 Physiological Ecology of Western Juniper and Associated Species ...................................... 17 Introduction ........................................... 17 Western Juniper — Patterns in Biomass Allocation............ 17 Western Juniper — Allocation Patterns of Carbon and -
Pije 14 Jeffrey Pine-Incense
PIJE 14 JEFFREY PINE-INCENSE-CEDAR/HUCKLEBERRY OAK Pinus jeffreyi-Calocedrus decurrens/Quercus vaccinifolia PIJE-CADE27/QUVA (N=13; FS=13) Distribution. This Association occurs on the Applegate and Ashland Ranger Districts, Rogue River National Forest and the Galice and Illinois Valley Ranger Districts, Siskiyou National Forest. It may also occur on the Ashland and Grants Pass Resource Areas, Medford District, Bureau of Land Management. Distinguishing Characteristics. This is a relatively high elevation Jeffrey pine association and is the coolest of the Jeffrey pine associations. Huckleberry oak and incense-cedar are usually present. Soils. Parent material is serpentine, with one occurrence of peridotite. Surface gravel and rock content averages 26 and 36 percent cover, respectively, while exposed bedrock cover averages 5 percent. Based on two plots sampled, soils are deep (greater than 40 inches) and well drained. Surface texture is silty clay loam, with 8 to 25 percent gravel, 35 to 50 percent cobbles and stones, and 32 percent PIJE 15 clay. Subsurface texture is silty clay loam, with 5 percent gravel, 40 percent cobbles and stones, and 32 to 35 percent clay. The soil moisture regime is probably xeric and the soil temperature regime is probably frigid. Soils classify to the following subgroups: Dystric Xerochrept and Typic Xerochrept. Environment. Elevation averages 3990 feet. Aspect is variable, although generally not northerly. Slope averages 33 percent with a range of 5 to 68 percent. Slope position ranges from ridgetops down to the middle one-third of the slope. Vegetation Composition and Structure. Total species richness is low for the Series, averaging 27 species. -
Proceedings of the 56 Annual Western International Forest Disease Work
Proceedings of the 56th Annual Western International Forest Disease Work Conference October 27-31, 2008 Missoula, Montana St. Marys Lake, Glacier National Park Compiled by: Fred Baker Department of Wildland Resources College of Natural Resources Utah State University Proceedings of the 56th Annual Western International Forest Disease Work Conference October 27 -31, 2008 Missoula, Montana Holiday Inn Missoula Downtown At The Park Compiled by: Fred Baker Department of Wildland Resources College of Natural Resources Utah State University & Carrie Jamieson & Patsy Palacios S.J. and Jessie E. Quinney Natural Resources Research Library College of Natural Resources Utah State University, Logan 2009, WIFDWC These proceedings are not available for citation of publication without consent of the authors. Papers are formatted with minor editing for formatting, language, and style, but otherwise are printed as they were submitted. The authors are responsible for content. TABLE OF CONTENTS Program Opening Remarks: WIFDWC Chair Gregg DeNitto Panel: Climate Change and Forest Pathology – Focus on Carbon Impacts of Climate Change for Drought and Wildfire Faith Ann Heinsch 3 Carbon Credit Projects in the Forestry Sector: What is Being Done to Manage Carbon? What Can Be Done? Keegan Eisenstadt 3 Mountain Pine Beetle and Eastern Spruce Budworm Impacts on Forest Carbon Dynamics Caren Dymond 4 Climate Change’s Influence on Decay Rates Robert L. Edmonds 5 Panel: Invasive Species: Learning by Example (Ellen Goheen, Moderator) Is Firewood Moving Tree Pests? William -
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. -
Psme 46 Douglas-Fir-Incense
PSME 46 DOUGLAS-FIR-INCENSE-CEDAR/PIPER'S OREGONGRAPE Pseudotsuga menziesii-Calocedrus decurrens/Berberis piperiana PSME-CADE27/BEPI2 (N=18; FS=18) Distribution. This Association occurs on the Applegate, Ashland, and Prospect Ranger Districts, Rogue River National Forest, and the Tiller and North Umpqua Ranger Districts, Umpqua National Forest. It may also occur on the Butte Falls Ranger District, Rogue River National Forest and adjacent Bureau of Land Management lands. Distinguishing Characteristics. This is a drier, cooler Douglas-fir association. White fir is frequently present, but with relatively low covers. Piper's Oregongrape and poison oak, dry site indicators, are also frequently present. Soils. Parent material is mostly schist, welded tuff, and basalt, with some andesite, diorite, and amphibolite. Average surface rock cover is 8 percent, with 8 percent gravel. Soils are generally deep, but may be moderately deep, with an average depth of greater than 40 inches. PSME 47 Environment. Elevation averages 3000 feet. Aspects vary. Slope averages 35 percent and ranges between 12 and 62 percent. Slope position ranges from the upper one-third of the slope down to the lower one-third of the slope. This Association may also occur on benches and narrow flats. Vegetation Composition and Structure. Total species richness is high for the Series, averaging 44 percent. The overstory is dominated by Douglas-fir and ponderosa pine, with sugar pine and incense-cedar common associates. Douglas-fir dominates the understory. Incense-cedar, white fir, and Pacific madrone frequently occur, generally with covers greater than 5 percent. Sugar pine is common. Frequently occurring shrubs include Piper's Oregongrape, baldhip rose, poison oak, creeping snowberry, and Pacific blackberry. -
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. -
Chestnut Growers' Guide to Site Selection and Environmental Stress
This idyllic orchard has benefited from good soil and irrigation. Photo by Tom Saielli Chestnut Growers’ Guide to Site Selection and Environmental Stress By Elsa Youngsteadt American chestnuts are tough, efficient trees that can reward their growers with several feet of growth per year. They’ll survive and even thrive under a range of conditions, but there are a few deal breakers that guarantee sickly, slow-growing trees. This guide, intended for backyard and small-orchard growers, will help you avoid these fatal mistakes and choose planting sites that will support strong, healthy trees. You’ll know you’ve done well when your chestnuts are still thriving a few years after planting. By then, they’ll be strong enough to withstand many stresses, from drought to a caterpillar outbreak, with much less human help. Soil Soil type is the absolute, number-one consideration when deciding where—or whether—to plant American chestnuts. These trees demand well-drained, acidic soil with a sandy to loamy texture. Permanently wet, basic, or clay soils are out of the question. So spend some time getting to know your dirt before launching a chestnut project. Dig it up, roll it between your fingers, and send in a sample for a soil test. Free tests are available through most state extension programs, and anyone can send a sample to the Penn State Agricultural Analytical Services Lab (which TACF uses) for a small fee. More information can be found at http://agsci.psu.edu/aasl/soil-testing. There are several key factors to look for. The two-foot-long taproot on this four- Acidity year-old root system could not have The ideal pH for American chestnut is 5.5, with an acceptable range developed in shallow soils, suggesting from about 4.5 to 6.5. -
Trees for Alkaline Soil Greg Paige, Arboretum Curator
RESEARCH LABORATORY TECHNICAL REPORT Trees for Alkaline Soil Greg Paige, Arboretum Curator Common name Scientific name Common name Scientific name Amur maple Acer ginnala Norway spruce Picea abies Hedge maple Acer campestre Serbian spruce Picea omorika Norway maple Acer platanoides Lacebark pine Pinus bungeana Paperbark maple Acer griseum Limber pine Pinus flexilis Tatarian maple Acer tatarian London plane tree Platanus x acerifolia European hornbeam Carpinus betulus Callery pear Pyrus calleryana Atlas cedar Cedrus atlantica (use cultivars) Cedar of Lebanon Cedrus libani Shingle oak Quercus imbricaria Deodar cedar Cedrus deodora Bur oak Quercus macrocarpa Hackberry Celtis occidentalis English oak Quercus robur Yellowwood Cladrastis lutea Littleleaf linden Tilia cordata Corneliancherry dogwood Cornus mas Silver linden Tilia tomentosa Cockspur hawthorn Crataegus crus-galli Lacebark elm Ulmus parvifolia Washington hawthorn Crataegus Japanese zelkova Zelkova serrata phaenopyrum Leyland cypress x Cupressocyparis leylandii Hardy rubber tree Eucommia ulmoides Green ash Fraxinus pennsylvanica Founded in 1926, The Bartlett Tree Research Ginkgo Ginkgo biloba Laboratories is the research wing of Bartlett Tree Thornless honeylocust Gleditsia triacanthos ‘inermis’ Experts. Scientists here develop guidelines for all of Kentucky coffeetree Gymnocladus dioicus the Company’s services. The Lab also houses a state- Goldenraintree Koelreuteria of-the-art plant diagnostic clinic and provides vital paniculata technical support to Bartlett arborists and field staff Amur maackia Maackia amurensis for the benefit of our clients. Crabapple Malus spp. Parrotia/Persian ironwood Parrotia persica Amur cork tree Phellodendron amurense Page 1 of 1 . -
Western Juniper Field Guide: Asking the Right Questions to Select Appropriate Management Actions
Western Juniper Field Guide: Asking the Right Questions to Select Appropriate Management Actions Circular 1321 U.S. Department of the Interior U.S. Geological Survey Cover: Photograph taken by Richard F. Miller. Western Juniper Field Guide: Asking the Right Questions to Select Appropriate Management Actions By R.F. Miller, Oregon State University, J.D. Bates, T.J. Svejcar, F.B. Pierson, U.S. Department of Agriculture, and L.E. Eddleman, Oregon State University This is contribution number 01 of the Sagebrush Steppe Treatment Evaluation Project (SageSTEP), supported by funds from the U.S. Joint Fire Science Program. Partial support for this guide was provided by U.S. Geological Survey Forest and Rangeland Ecosystem Science Center. Circular 1321 U.S. Department of the Interior U.S. Geological Survey U.S. Department of the Interior DIRK KEMPTHORNE, Secretary U.S. Geological Survey Mark D. Myers, Director U.S. Geological Survey, Reston, Virginia: 2007 For product and ordering information: World Wide Web: http://www.usgs.gov/pubprod Telephone: 1-888-ASK-USGS For more information on the USGS--the Federal source for science about the Earth, its natural and living resources, natural hazards, and the environment: World Wide Web: http://www.usgs.gov Telephone: 1-888-ASK-USGS Any use of trade, product, or firm names is for descriptive purposes only and does not imply endorsement by the U.S. Government. Although this report is in the public domain, permission must be secured from the individual copyright owners to reproduce any copyrighted materials con- tained within this report. Suggested citation: Miller, R.F., Bates, J.D., Svejcar, T.J., Pierson, F.B., and Eddleman, L.E., 2007, Western Juniper Field Guide: Asking the Right Questions to Select Appropriate Management Actions: U.S. -
Sample Planting Grids All Chestnuts in the Planting Must Have Permanent Embossed Numerical Tags for That Planting and Will Be Monitored by That Tag
Sample planting grids All chestnuts in the planting must have permanent embossed numerical tags for that planting and will be monitored by that tag. The basic module is 6 x 6 ft spacing with a minimum of 20 ft borders. Such plantings allow easy fencing and mowing. Rows and columns need not be continuous nor do they need to be the same length. Mapping should show gaps. Create a simple schematic map of the planting once done. These configurations can be modified in a wide variety of ways but if lengthened in either direction, a depth of a least 3 rows in any dimension should be maintained. Remember that the pines are an early succession planting designed to create early site coverage and encourage upward growth in hardwoods. Their removal will be a first step in thinning. Different configurations will impose other thinning regimens over time: for example, red oaks might be removed in #1 over time if there is high chestnut survival and vigorous growth. These plantings are designed to introduce at least 30 chestnuts on the site. These should represent at least 2‐3 chestnut families, and may include Kentucky stump sprout families. #1. Alternate row planting 024 ft 30 ft 36 ft 42 ft 48 ft 54 ft 60 ft 66 ft 72 ft 78 ft 98 ft Dimensions 24 ft Pine Chestnut Pine Red Oak Pine Chestnut Pine Red Oak Pine Red Oak 110 x 98 ft 10780 sq ft 30 ft Pine Red Oak Pine Chestnut Pine Red Oak Pine Chestnut Pine Chestnut 36 ft Pine Chestnut Pine Red Oak Pine Chestnut Pine Red Oak Pine Red Oak Acreage 42 ft Pine Red Oak Pine Chestnut Pine Red Oak Pine Chestnut -
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