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Appendix Intermediate Intermediate None High None 2000 2000 2000 2000 2000 Abies alba Abies homolepis Acer barbinerve Acer campestre Acer ginnala 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 ● ● ● 500 500 500 500 500 ● ● ● NL ● ● ● ● ● ● ● ● 0 0 0 0 0 Laube et al. 2014 Laube et al. 2014 This study This study This study Intermediate Intermediate Highv High High 2000 2000 2000 2000 2000 Acer negundo Acer platanoides Acer pseudoplatanus Acer rubrum Acer saccharinum 1500 1500 1500 1500 1500 NL NL ● 1000 1000 1000 1000 1000 ● ● ● ● ● ● 500 500 500 500 NL NL ● 500 ● ● ● 0 0 0 0 0 Laube et al. 2014 This study Laube et al. 2014 Polgar 2014 Polgar 2014 High Intermediate Highv Intermediate High 2000 2000 2000 2000 2000 Acer saccharum Acer tataricum Aesculus flava Aesculus hippocastanum Aesculus parviflora 1500 1500 1500 ● 1500 1500 ● 1000 1000 1000 1000 1000 NL ● ● ● ● ● ● 500 500 500 500 ● 500 ● ● ● ● ● 0 0 0 0 0 Laube et al. 2014 Laube et al. 2014 This study This study This study Intermediate None vHigh Intermediate Intermediate 2000 2000 2000 2000 2000 Alnus incana Alnus maximowiczii Alnus serrulata Amelanchier alnifolia Amelanchier florida 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 ● ● ● ● ● ● NL NL ● ● 500 ● 500 500 500 ● 500 ● ● ● 0 0 0 0 0 This study This study Polgar 2014 This study This study Intermediate None vHigh None None 2000 2000 2000 2000 2000 Amelanchier laevis Amorpha fruticosa Aronia arbutifolia Aronia melanocarpa Berberis dielsiana 1500 1500 1500 1500 1500 ● 1000 1000 1000 1000 1000 ● ● ● 500 ● ● 500 500 500 500 ● ● ● ● ● ● ● ● ● 0 0 0 0 0 This study Laube et al. 2014 Polgar 2014 This study This study Intermediate None v High High High 2000 2000 2000 2000 2000 Berberis thunbergii Berberis vulgaris Betula lenta Betula nana Betula papyrifera 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 ● ● ● ● ● ● ● 500 500 ● 500 500 500 ● ● ● ● ● ● ● 0 C1 C2 C3 0 C1 C2 C3 0 C1 C2 C3 0 C1 C2 C3 0 C1 C2 C3 Polgar 2014 Polgar 2014 This study This study Polgar 2014 132" v 133" Figure S11 partial Figure S1 partial 134" 135" 136" IntermediateIntermediate None NoneNone NoneNone NoneNone 20002000 20002000 20002000 20002000 20002000 BetulaBetula pendulapendula BetulaBetula populifoliapopulifolia BuddlejaBuddleja albifloraalbiflora BuddlejaBuddleja alternifoliaalternifolia BuddlejaBuddleja davidiidavidii 15001500 15001500 15001500 15001500 15001500 10001000 10001000 10001000 10001000 10001000 500500 500500 ● 500500 500500 500500 ●● ● ●● ●● ● ●● ●● ● ● ● ●● ●● ●● ●● ●● ● 00 00 00 00 00 LaubeLaube etet al.al. 20142014 ThisThis studystudy ThisThis study study ThisThis study study ThisThis study study v None IntermediateIntermediate IntermediateIntermediate NoneNone HighHigh 20002000 20002000 20002000 20002000 20002000 CaraganaCaragana pygmaeapygmaea CarpinusCarpinus betulusbetulus CarpinusCarpinus laxifloralaxiflora CarpinusCarpinus monbeigianamonbeigiana CaryaCarya cordiformiscordiformis 15001500 15001500 15001500 15001500 15001500 10001000 10001000 10001000 10001000 10001000 ●● ●● ●● ●● ●● ●● ●● 500 500 ●● 500 ● 500 ●● 500 500 500 ●● 500 ● 500 500 ●● ●● ●● ●● 00 00 00 00 00 ThisThis studystudy ThisThis studystudy ThisThis study study ThisThis study study ThisThis study study High High HighHighv NoneNone IntermediateIntermediate 20002000 20002000 20002000 20002000 20002000 CaryaCarya glabraglabra CaryaCarya laciniosalaciniosa CaryaCarya ovataovata CastaneaCastanea sativasativa CedrusCedrus libanilibani ●● ●● 15001500 15001500 ●● 15001500 15001500 15001500 ●● 10001000 10001000 10001000 10001000 10001000 ●● ●● ●● ●● ●● ●● ●● ●● 500500 NL NL ●● 500500 500500 500500 500500 00 00 00 00 00 PolgarPolgar 20142014 ThisThis studystudy ThisThis study study ThisThis study study ThisThis study study IntermediateIntermediate IntermediateIntermediate vHighHigh HighHigh IntermediateIntermediate 20002000 20002000 20002000 20002000 20002000 CelastrusCelastrus orbiculatusorbiculatus CeltisCeltis caucasicacaucasica CeltisCeltis laevigatalaevigata CeltisCeltis occidentalisoccidentalis CephalanthusCephalanthus occidentalisoccidentalis 15001500 15001500 15001500 15001500 15001500 10001000 10001000 10001000 10001000 ●● 10001000 ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● ●● 500500 500500 ●● 500500 500500 500500 00 00 00 00 00 PolgarPolgar 20142014 ThisThis studystudy ThisThis study study ThisThis study study ThisThis study study IntermediateIntermediate High vHighHigh NoneNone HighHigh 20002000 20002000 20002000 20002000 20002000 CercidiphyllumCercidiphyllum japonicumjaponicum CercidiphyllumCercidiphyllum magnificummagnificum CercisCercis canadensiscanadensis CercisCercis chinensischinensis CladrastisCladrastis lutealutea 15001500 15001500 15001500 15001500 15001500 10001000 10001000 10001000 10001000 10001000 ●● ●● ●● ●● ●● ●● ●● ●● ● ●● ● ●● 500500 ●● ●● 500500 ●● 500500 500500 500500 ●● 00 00 00 00 00 ThisThis studystudy ThisThis studystudy ThisThis study study ThisThis study study ThisThis study study High High IntermediateIntermediate IntermediateIntermediate NoneNone 20002000 20002000 20002000 20002000 20002000 ClethraClethra alnifoliaalnifolia ComptoniaComptonia peregrinaperegrina CornusCornus albaalba CornusCornus amomumamomum CornusCornus kousakousa 15001500 15001500 15001500 15001500 15001500 10001000 10001000 10001000 10001000 10001000 NL ●● ●● ●● NL ●● ●● ●● ●● ●● ●● 500500 ●● 500500 ●● 500500 ●● 500500 ●● 500500 00 C1 C2 C3 0 0 C1 C2 C3 0 0 C1 C2 C3 0 0 C1 C2 C3 0 0 C1 C2 C3 137" Polgar Polgar 20142014 PolgarPolgar 20142014 ThisThis study study PolgarPolgar 2014 2014 ThisThis study study 138" Figure S11 continued Figure S1 continued 139" 140" 141" None None None Intermediate None 2000 2000 2000 2000 2000 Cornus mas Corylopsis sinensis Corylopsis spicata Corylus americana Corylus avellana 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 ● ● ● 500 500 ● ● 500 ● 500 500 ● ● ● ● ● ● ● ● ● 0 0 0 0 0 Laube et al. 2014 This study This study Polgar 2014 This study Intermediate Intermediate Intermediate None None 2000 2000 2000 2000 2000 Corylus heterophylla Corylus sieboldiana Decaisnea fargesii Deutzia gracilis Deutzia scabra 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 ● ● ● 500 500 500 ● 500 500 ● ● ● ● ● ● ● ● ● ● ● 0 0 0 0 0 This study This study This study This study This study None None None None None 2000 2000 2000 2000 2000 Elaeagnus umbellata Elaeagnus ebbingei Eleutherococcus senticosus Eleutherococcus setchuensis Eleutherococcus sieboldianus 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 500 500 500 500 ● 500 ● ● ● ● ● ● ● ● ● ● ● ● ● ● 0 0 0 0 0 Polgar 2014 This study This study This study This study Intermediate Intermediate High High High 2000 2000 2000 2000 2000 Euonymus alatus Euonymus europaeus Euonymus latifolius Fagus crenata Fagus engleriana 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 ● ● ● ● NL ● ● ● 500 ● 500 ● 500 500 500 ● ● ● ● ● 0 0 0 0 0 Polgar 2014 This study This study This study This study High High High None None 2000 2000 2000 2000 2000 Fagus grandifolia Fagus orientalis Fagus sylvatica Forsythia ovata Forsythia suspensa 1500 1500 1500 1500 1500 ● NL NL ● 1000 1000 1000 1000 1000 ● ● ● 500 500 ● 500 500 500 ● ● ● ● ● ● ● 0 0 0 0 0 Polgar 2014 This study This study This study This study Intermediate Intermediate None Intermediate High 2000 2000 2000 2000 2000 Fraxinus americana Fraxinus chinensis Fraxinus excelsior Fraxinus latifolia ● Fraxinus ornus 1500 1500 1500 1500 1500 ● 1000 1000 1000 1000 1000 ● ● ● ● NL ● ● ● ● 500 500 ● 500 ● 500 500 ● ● 0 C1 C2 C3 0 C1 C2 C3 0 C1 C2 C3 0 C1 C2 C3 0 C1 C2 C3 142" Polgar 2014 Laube et al. 2014 Laube et al. 2014 This study This study 143" FigureFigure S11 S1 continuedcontinued 144" 145" 146" None High Intermediate Intermediate High 2000 2000 2000 2000 2000 Fraxinus pensylvanica Gaylussacia baccata Ginkgo biloba Hamamelis japonica Hamamelis vernalis 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 ● ● ● ● ● ● ● ● 500 ● 500 ● 500 500 500 ● ● ● ● ● 0 0 0 0 0 Laube et al. 2014 Polgar 2014 This study This study This study High None None Intermediate Intermediate 2000 2000 2000 2000 2000 Hamamelis viginiana Heptacodium miconioides Hibiscus syriacus Hydrangea arborescens Hydrangea involucrata 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 ● ● ● ● ● 500 ● 500 500 ● 500 500 ● ● ● ● ● ● ● ● 0 0 0 0 0 Polgar 2014 This study This study This study This study Intermediate Intermediate Intermediate Intermediate Intermediate 2000 2000 2000 2000 2000 Hydrangea serrata Juglans ailantifolia Juglans cinerea Juglans regia Kalmia angustifolia 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 ● ● ● ● ● ● 500 500 500 ● 500 ● 500 NL ● ● ● ● ● ● 0 0 0 0 0 This study Laube et al. 2014 Laube et al. 2014 Laube et al. 2014 Polgar 2014 High None Intermediate Intermediate None 2000 2000 2000 2000 2000 Kalmia latifolia Larix decidua Larix gmelinii Larix kaempferi Ligustrum compactum 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 NL NL ● ● 500 500 500 500 ● 500 ● ● ● ● ● ● ● ● ● ● 0 0 0 0 0 Polgar 2014 Laube et al. 2014 This study This study Polgar 2014 None None High None Intermediate 2000 2000 2000 2000 2000 Ligustrum ibota Ligustrum tschonoskii Lindera benzoin Liquidambar orientalis Liquidambar styraciflua 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 NL NL ● ● ● ● 500 500 500 500 ● 500 ● ● ● ● ● ● ● ● 0 0 0 0 0 Polgar 2014 This study Polgar 2014 This study This study Intermediate None None None None 2000 2000 2000 2000 2000 Liriodendron tulipifera Lonicera alpigena Lonicera caerulea Lonicera maackii Lonicera maximowiczii 1500 1500 1500 1500 1500 1000 1000 1000 1000 1000 ● 500 500
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    Vegetation Unit Summaries for Springwater Corridor (SCOR) Report date: 3/27/2007 '*' = non-native invasive species Visit data as of: 3/27/2007 Unit rSCOR*104 Size: 0.16 Acres NVCS Subclass: Deciduous forest % Tree canopy: 60% % Non-Native Cover: 90 Slope: na Aspect: na Visit date: 8/2/2006 Wetland indicators: Streams, Hydrophilic Vegetation. (Surface water was present) Dominant Trees: red alder (Alnus rubra). Dominant Shrubs: Himalayan blackberry (Rubus discolor*). Shrubs > 20% cover: red-osier dogwood (Cornus sericea ssp. sericea). Dominant Grasses: reed canarygrass (Phalaris arundinacea* > 50% cover). Additional Invasives: yellow flag iris (Iris pseudacorus*), bittersweet nightshade (Solanum dulcamara*). Ecological Health: Fair. Primary Management concerns: heavy level of invasive species, Stream Bank Erosion. Unit rSCOR*105 Size: 7.54 Acres NVCS Subclass: Deciduous woodland % Tree canopy: 55% % Non-Native Cover: 90 Slope: na Aspect: na Visit date: 8/2/2006 Wetland indicators: Streams, Hydrophilic Vegetation. (Surface water was present) Dominant Trees: red alder (Alnus rubra). Dominant Shrubs: Himalayan blackberry (Rubus discolor*). Shrubs > 20% cover: red-osier dogwood (Cornus sericea ssp. sericea). Dominant Grasses: reed canarygrass (Phalaris arundinacea* > 50% cover). Additional Invasives: yellow flag iris (Iris pseudacorus*), bittersweet nightshade (Solanum dulcamara*). Ecological Health: Fair. Primary Management concerns: heavy level of invasive species, Stream Bank Erosion. Unit rSCOR*108 Size: 0.32 Acres NVCS Subclass: Deciduous woodland % Tree canopy: 40% % Non-Native Cover: 90 Slope: na Aspect: na Visit date: 8/2/2006 Wetland indicators: Streams, Hydrophilic Vegetation. (Surface water was present) Dominant Trees: red alder (Alnus rubra). Dominant Shrubs: Himalayan blackberry (Rubus discolor*). Dominant Grasses: reed canarygrass (Phalaris arundinacea* > 50% cover).
  • Species at Risk on Department of Defense Installations

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    Species at Risk on Department of Defense Installations Revised Report and Documentation Prepared for: Department of Defense U.S. Fish and Wildlife Service Submitted by: January 2004 Species at Risk on Department of Defense Installations: Revised Report and Documentation CONTENTS 1.0 Executive Summary..........................................................................................iii 2.0 Introduction – Project Description................................................................. 1 3.0 Methods ................................................................................................................ 3 3.1 NatureServe Data................................................................................................ 3 3.2 DOD Installations............................................................................................... 5 3.3 Species at Risk .................................................................................................... 6 4.0 Results................................................................................................................... 8 4.1 Nationwide Assessment of Species at Risk on DOD Installations..................... 8 4.2 Assessment of Species at Risk by Military Service.......................................... 13 4.3 Assessment of Species at Risk on Installations ................................................ 15 5.0 Conclusion and Management Recommendations.................................... 22 6.0 Future Directions.............................................................................................
  • Landscape Standards 11

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    LANDSCAPE STANDARDS 11 Section 11 describes the landscape guidelines and standards for the Badger Mountain South community. 11.A Introduction.................................................11-2 11.B Guiding Principles..............................................11-2 11.C Common Standards Applicable to all Districts......11-3 11.D Civic and Commercial District Standards................11-4 11.E Residential Standards........................................11-4 11.F Drought Tolerant and/or Native/Naturalized Plant List ......................................................11-5 - 11-11 11.G Refined Plant List....................................11-12 - 11-15 Issue Date: 12-07-10 Badger Mountain South: A Walkable and Sustainable Community, Richland, WA 11-1 11.A INTRODUCTION 11.B GUIDING PRINCIPLES The landscape guidelines and standards which follow are intended to complement the natural beauty of the Badger Mountain Preserve, help define the Badger Mountain South neighborhoods and commercial areas and provide a visually pleasant gateway into the City of Richland. The landscape character of the Badger Mountain South community as identified in these standards borrows heavily from the precedent of the original shrub-steppe landscape found here. However that historical character is joined with other opportunities for a more refined and urban landscape pattern that relates to edges of uses and defines spaces into activity areas. This section is divided into the following sub-sections: Guiding Principles, which suggest the overall orientation for all landscape applications; Common Standards, which apply to all Districts; District-specific landscape standards; and finally extensive plant lists of materials suitable in a variety of situations. 1. WATER CONSERVATION WATER CONSERVATION continued 2. REGIONAL LANDSCAPE CHARACTER a. Drought tolerant plants. d. Design for low maintenance. a.