Appendix M—Wildlife Biological Evaluation
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												  Natural Regeneration of White and Red Fir. . . Influence of Several Factors. Berkeley, Calif., Pacific SWPACIFIC 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.
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												  Oaks (Quercus Spp.): a Brief HistoryPublication WSFNR-20-25A April 2020 Oaks (Quercus spp.): A Brief History Dr. Kim D. Coder, Professor of Tree Biology & Health Care / University Hill Fellow University of Georgia Warnell School of Forestry & Natural Resources Quercus (oak) is the largest tree genus in temperate and sub-tropical areas of the Northern Hemisphere with an extensive distribution. (Denk et.al. 2010) Oaks are the most dominant trees of North America both in species number and biomass. (Hipp et.al. 2018) The three North America oak groups (white, red / black, and golden-cup) represent roughly 60% (~255) of the ~435 species within the Quercus genus worldwide. (Hipp et.al. 2018; McVay et.al. 2017a) Oak group development over time helped determine current species, and can suggest relationships which foster hybridization. The red / black and white oaks developed during a warm phase in global climate at high latitudes in what today is the boreal forest zone. From this northern location, both oak groups spread together southward across the continent splitting into a large eastern United States pathway, and much smaller western and far western paths. Both species groups spread into the eastern United States, then southward, and continued into Mexico and Central America as far as Columbia. (Hipp et.al. 2018) Today, Mexico is considered the world center of oak diversity. (Hipp et.al. 2018) Figure 1 shows genus, sub-genus and sections of Quercus (oak). History of Oak Species Groups Oaks developed under much different climates and environments than today. By examining how oaks developed and diversified into small, closely related groups, the native set of Georgia oak species can be better appreciated and understood in how they are related, share gene sets, or hybridize.
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												  F.3 References for Appendix FF-1 APPENDIX F: ECOREGIONS OF THE 11 WESTERN STATES AND DISTRIBUTION BY ECOREGION OF WIND ENERGY RESOURCES ON BLM-ADMINISTERED LANDS WITHIN EACH STATE F-2 F-3 APPENDIX F: ECOREGIONS OF THE 11 WESTERN STATES AND DISTRIBUTION BY ECOREGION OF WIND ENERGY RESOURCES ON BLM-ADMINISTERED LANDS WITHIN EACH STATE F.1 DESCRIPTIONS OF THE ECOREGIONS Ecoregions delineate areas that have a general similarity in their ecosystems and in the types, qualities, and quantities of their environmental resources. They are based on unique combinations of geology, physiography, vegetation, climate, soils, land use, wildlife, and hydrology (EPA 2004). Ecoregions are defined as areas having relative homogeneity in their ecological systems and their components. Factors associated with spatial differences in the quality and quantity of ecosystem components (including soils, vegetation, climate, geology, and physiography) are relatively homogeneous within an ecoregion. A number of individuals and organizations have characterized North America on the basis of ecoregions (e.g., Omernik 1987; CEC 1997; Bailey 1997). The intent of such ecoregion classifications has been to provide a spatial framework for the research, assessment, management, and monitoring of ecosystems and ecosystem components. The ecoregion discussions presented in this programmatic environmental impact statement (PEIS) follow the Level III ecoregion classification based on Omernik (1987) and refined through collaborations among U.S. Environmental Protection Agency (EPA) regional offices, state resource management agencies, and other federal agencies (EPA 2004). The following sections provide brief descriptions of each of the Level III ecoregions that have been identified for the 11 western states in which potential wind energy development may occur on BLM-administered lands.
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												  Giant Sequoia Insect, Disease, and Ecosystem Interactions1Giant 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.
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												  Cercocarpus Montanus Cercocarpus Montanus ‘USU-CEMO-001’ ‘USU-CEMO- Was Collected As a Suspected Dwarf Plant in TM Moffat County, CO, on 20 June 2014HORTSCIENCE 55(11):1871–1875. 2020. https://doi.org/10.21273/HORTSCI15343-20 Origin Cercocarpus montanus Cercocarpus montanus ‘USU-CEMO-001’ ‘USU-CEMO- was collected as a suspected dwarf plant in TM Moffat County, CO, on 20 June 2014. This 001’: A New Sego Supreme Plant unique, procumbent specimen was discovered laying over a rock on a windy ridge at an Asmita Paudel, Youping Sun, and Larry A. Rupp elevation of 2708 m (Fig. 2A). The appearance Center for Water Efficient Landscaping, Department of Plants, Soils, and looked different from the typical C. montanus Climate, Utah State University, 4820 Old Main Hill, Logan, UT 84322 nearby (Fig. 2B). The leaves are smaller and narrower with less serrations compared with Richard Anderson the typical plants (Fig. 2C). Healthy cuttings USU Botanical Center, 725 Sego Lily Drive, Kaysville, UT 84037 were collected, wrapped in moist newspapers and placed on ice until transferred to a cooler at Additional index words. alder-leaf mountain mahogany, cutting propagation, landscape plant, 4 °C. On 21 June, the terminal cuttings were native plant, true mountain mahogany rinsed in 1% ZeroTol (27.1% hydrogen diox- ide, 2.0% peroxyacetic acid, 70.9% inert in- gredient; BioSafe Systems, Hartford, CT), Sego SupremeTM is a plant introduction mose style with elongated achenes wounded by scraping 1 cm of bark from the program developed by the Utah State Uni- (Fig. 1B) (Shaw et al., 2004). It possesses base of the cutting on one side, treated with versity (USU) Botanical Center (Anderson an extensive root system and adapts to 2000 mg·L–1 indole-3-butyric acid (IBA)/1000 et al., 2014) to introduce native and adaptable medium to coarse textured soil.
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												  Hybridization of the California FirsForest 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.
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												  Local Variation in Intergrading Abies Grandis—Abies Concolor Populations in the Central Oregon Cascades: Needle Morphology and Periderm ColorBOT. 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.
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												  A Trip to Study Oaks and Conifers in a Californian Landscape with the International Oak SocietyA Trip to Study Oaks and Conifers in a Californian Landscape with the International Oak Society Harry Baldwin and Thomas Fry - 2018 Table of Contents Acknowledgments ....................................................................................................................................................... 3 Introduction .................................................................................................................................................................. 3 Aims and Objectives: .................................................................................................................................................. 4 How to achieve set objectives: ............................................................................................................................................. 4 Sharing knowledge of experience gained: ....................................................................................................................... 4 Map of Places Visited: ................................................................................................................................................. 5 Itinerary .......................................................................................................................................................................... 6 Background to Oaks .................................................................................................................................................... 8 Cosumnes River Preserve ........................................................................................................................................
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												  Abies Concolor (White Fir)Compiled here is distribution, characteristics and other information on host species featured as ‘Host of the Month’ in past issues of the COMTF Monthly Report. Abies concolor (white fir) This is an evergreen tree native to the mountains of southern Oregon, California, the southern Rocky Mountains, and Baja California. Large and symmetrical, white fir grows 80 – 120ft tall and 15 – 20ft wide in its native range and in the Pacific Northwest. White fir is one of the top timber species found in the Sierra Nevada Mountains of CA and is a popular Christmas tree, as well as one of the most commonly grown native firs in Western gardens. Young trees are conical in shape, but develop a dome-like crown with age. The flattened needles of white fir are silvery blue-green, blunt at the tip , and grow 2 – 3in long. Often curving upwards, the needles extend at right angles from the twig, and twigs produce a citrus smell when needles are broken. White fir is monoecious, producing yellow- to red-toned, catkin-like male flowers and inconspicuous yellow-brown female flowers. The oblong cones grow 3 – 5 in upright, are yellow-green to purple in color, and are deciduous at maturity, dispersing seed in the fall. New twigs are dark- orange, but become gray-green, then gray with maturity. The bark of saplings is thin, smooth, and gray, turning thick, ash-gray with age, and developing deep irregular furrows. P. ramorum- infected Abies concolor (white fir) was first reported in the October 2005 COMTF newsletter as having been found at a Christmas tree farm in the quarantined county of Santa Clara.
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												  List of Plants for Great Sand Dunes National Park and PreserveGreat Sand Dunes National Park and Preserve Plant Checklist DRAFT as of 29 November 2005 FERNS AND FERN ALLIES Equisetaceae (Horsetail Family) Vascular Plant Equisetales Equisetaceae Equisetum arvense Present in Park Rare Native Field horsetail Vascular Plant Equisetales Equisetaceae Equisetum laevigatum Present in Park Unknown Native Scouring-rush Polypodiaceae (Fern Family) Vascular Plant Polypodiales Dryopteridaceae Cystopteris fragilis Present in Park Uncommon Native Brittle bladderfern Vascular Plant Polypodiales Dryopteridaceae Woodsia oregana Present in Park Uncommon Native Oregon woodsia Pteridaceae (Maidenhair Fern Family) Vascular Plant Polypodiales Pteridaceae Argyrochosma fendleri Present in Park Unknown Native Zigzag fern Vascular Plant Polypodiales Pteridaceae Cheilanthes feei Present in Park Uncommon Native Slender lip fern Vascular Plant Polypodiales Pteridaceae Cryptogramma acrostichoides Present in Park Unknown Native American rockbrake Selaginellaceae (Spikemoss Family) Vascular Plant Selaginellales Selaginellaceae Selaginella densa Present in Park Rare Native Lesser spikemoss Vascular Plant Selaginellales Selaginellaceae Selaginella weatherbiana Present in Park Unknown Native Weatherby's clubmoss CONIFERS Cupressaceae (Cypress family) Vascular Plant Pinales Cupressaceae Juniperus scopulorum Present in Park Unknown Native Rocky Mountain juniper Pinaceae (Pine Family) Vascular Plant Pinales Pinaceae Abies concolor var. concolor Present in Park Rare Native White fir Vascular Plant Pinales Pinaceae Abies lasiocarpa Present
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												  Blue Oak Plant Communities of Southern~ United States ~ Department Blue Oak Plant Communities of Southern of Agriculture Forest Service San Luis Obispo and Northern Santa Bar Pacific Southwest Research Station bara Counties, California General Technical Report PSW-GTR-139 Mark I. Borchert Nancy D.Cunha Patricia C. Kresse Marcee L. Lawrence Borchert. M:1rk I.: Cunha. N,mcy 0.: Km~,e. Patr1c1a C.: Lawrence. Marcec L. 1993. Blue oak plan! communilies or:.outhern San Luis Ob L<ipo and northern Santa Barbara Counties, California. Gen. Tech. Rep. PSW-GTR-139. Albany. CA: P:u:ilic Southwest Rcsc:arch Stution. Forest Service. U.S. Dcpurtment of Agriculture: 49 p. An ccologic:11clu,-sili.::uion '),,cm h:b Ileen developed for the Pacifil' Southwest Region of the Forest Service. As part of that c1a....,11ica1ion effort. blue oak rQ11('rrn., tlo11i;lusi1 / woodlands and forests ol ~out hem San Lub Ohi,po and northern Santa Barham Countie, in LO!> Padre!> Nationul Forest were cl:",ilicd imo i.\ plant communitic, using vegetation colkctcd from 208 plot:.. 0. 1 acre e:ach . Tim.'<.' di,tinct region, of vegetation were 1dentilicd 111 the ,tudy :1rea: Avcn:1lc,. Mirnndn Pinc Moun11,ln :ind Branch Mountnin. Communitie.., were dassilied ,eparntel) for plot, in each region. Each region ha, n woodland community thut occupies 11:u orgently slopmg bcnt·he..,.1oc,lopc~. and valley bo110111s. Thc,:c rnmmunitics possess a reltuivcly high proportion oflarge trcc, ( 2: I!( an. d.b.h.l 311d appcarro be heavily gnu cd. In s•ach region an extensive woodland or fore,t communit) covers modcr:uc , lope, with low ,olar in,ol:11io11 .
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												  Leptoglossus Occidentalis (Heidemann, 1910) Is an Invasive Insect SpeciesBartın Orman Fakültesi Dergisi 2012, Cilt: 14,Sayı: 21, 56-61 ISSN: 1302-0943 EISSN: 1308-5875 LEPTOGLOSSUS OCCIDENTALIS (HEIDEMANN, 1910) IS AN INVASIVE INSECT SPECIES Erdem HIZAL1*, Muhittin İNAN2 1) Istanbul Univesity, Faculty of Forestry, Department of Forest Entomology and Protection 2) Istanbul Univesity, Faculty of Forestry, Department of Surveying and Cadastre * Correspending Author: [email protected] ABSTRACT The western conifer seed bug, Leptoglossus occidentalis (Heidemann, 1910) (Heteroptera: Coreidae), is an invasive alien species of North American origin. In Europe, it was first collected in Italy in 1999. From there, it quickly expanded its range to western and eastern Europe. Leptoglossus occidentalis was recorded for the first time in Sariyer-Istanbul, Turkey in 2009. Leptoglossus occidentalis is specialised to conifers. In this study gives Leptoglossus occidentalis morphology, distribution and host plants, economic importance. Keywords: Leptoglossus occidentalis, insect, invasive İSTİLACI BİR BÖCEK TÜRÜ LEPTOGLOSSUS OCCIDENTALIS (HEIDEMANN, 1910) ÖZET Leptoglossus occidentalis (Heidemann, 1910) (Heteroptera: Coreidae) Kuzey Amerika orijinli istilacı yabancı bir böcek türüdür. Avrupa’da ilk defa 1999 yılında İtalya’da görülmüştür. Daha sonra hızla doğu ve batı Avrupa’ya yayılmıştır. Türkiye’de 2009 yılında Sarıyer-İstanbul’da tespit edilmiştir. İğne yapraklı ağaçları tercih eden bir zararlıdır. Bu çalışmada Leptoglossus occidentalis’in morfolojisi, yayılışı ve konukçu bitkileri ile ekonomik önemi anlatılmıştır. Anahtar Kelimeler: Leptoglossus occidentalis, böcek, istilacı 1. INTRODUCTION Coreidae (Leach 1815, superfamily Coreidea) includes 2200 species belonging to 500 genera worldwide, and has a very wide distribution. In the Palaearctic Region, 344 species in 84 genera have been listed (Dolling, 2006). In Turkey, 48 species from 20 genera have been recorded (Dursun, 2011).