Hands Creek Farm Nature Preserve Management Plan
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Pinus Echinata Shortleaf Pine
PinusPinus echinataechinata shortleafshortleaf pinepine by Dr. Kim D. Coder, Professor of Tree Biology & Health Care Warnell School of Forestry & Natural Resources, University of Georgia One of the most widespread pines of the Eastern United Sates is Pinus echinata, shortleaf pine. Shortleaf pine was identified and named in 1768. The scientific name means a “prickly pine cone tree.” Other common names for shortleaf pine include shortstraw pine, yellow pine, Southern yellow pine, shortleaf yellow pine, Arkansas soft pine, Arkansas pine, and old field pine. Among all the Southern yellow pines it has the greatest range and is most tolerant of a variety of sites. Shortleaf pine grows Southeast of a line between New York and Texas. It is widespread in Georgia except for coastal coun- ties. Note the Georgia range map figure. Pinus echinata is found growing in many mixtures with other pines and hardwoods. It tends to grow on medium to dry, well-drained, infertile sites, as compared with loblolly pine (Pinus taeda). It grows quickly in deep, well-drained areas of floodplains, but cannot tolerate high pH and high calcium concentrations. Compared with other Southern yellow pines, shortleaf is less demanding of soil oxygen content and essential element availability. It grows in Hardiness Zone 6a - 8b and Heat Zone 6-9. The lowest number of Hardiness Zone tends to delineate the Northern range limit and the largest Heat Zone number tends to define the South- ern edge of the range. This native Georgia pine grows in Coder Tree Grow Zone (CTGZ) A-D (a mul- tiple climatic attribute based map), and in the temperature and precipitation cluster based Coder Tree Planting Zone 1-6. -
Important Food Plants for Backyard Songbirds of the Catskills
Important Food Plants for Backyard Songbirds of the Catskills Woody Plants ****25-50%, ***10-25% of diet **5-10%, *2-5&% of diet 0.5-2% of diet Maples Box-elder Acer negundo Evening Grosbeak **** Coccothraustes vespertinus American Goldfinch Carduelis tristis Moosewood Acer pensylvanicum Purple Finch * Carpodacus purpureus Yellow-bellied Sapsucker (sap) Sphyrapicus varius Red Maple Acer rubrum Rose-breasted Grosbeak * Pheucticus ludovicianus Silver Maple Acer saccharinum Red-breasted Nuthatch * Sitta canadensis Sugar Maple Acer saccharum Mountain Maple Acer spicatum Serviceberries Downy Serviceberry Amelanchier arborea Cedar Waxwing * Bombicilla cedrorum Tufted Titmouse Baeolophus bicolor Shadblow Serviceberry Amelanchier canadensis Veery * Catharus fuscescens Northern Cardinal Cardinalis cardinalis Smooth Serviceberry Amelanchier laevis Hermit Thrush * Catharus guttatus Hermit Thrush Catharus guttatus Running Serviceberry Amelanchier stolonifera Gray Catbird * Dumetella carolinensis Northern Flicker Coraptes auratus Baltimore Oriole * Icterus galbula American Crow Corvus brachyrhyncos Blue Jay Cyanocitta cristata Wood Thrush Hylocichla mustelina Northern Mockingbird Mimus polyglottus Eastern Towhee Papilo erythrophthalmus Rose-breasted Grosbeak Pheucticus ludovicianus Downy Woodpecker Picoides pubescens Hairy Woodpecker Picoides villosus Scarlet Tanager Piranga olivacea Black-capped Chickadee Poecile atricapillus Eastern Bluebird Sialia sialis Brown Thrasher Toxostoma rufin American Robin Turdus migratorius Aralias Bristly Sarsparilla -
Glenn Oakes Bioblitz Report
Glen Oakes BioBlitz Report Note: The black line in the map denotes Glen Oakes Town Forest in Fremont, N.H. From May, 2011 Glenn Oakes Bioblitz 2011 page 2 of 11 whk Introduction On and around the weekend of May 21, 2011, an intensive species inventory (BioBlitz) was made in Fremont, NH within the Glen Oakes Town Forest. The event was organized to enhance the baseline information of the biodiversity found in this area begun by Forester Charles A. Moreno. Three small teams of volunteers lead by experts spent the morning of Saturday, May 21, 2011 scouring the Glen Oakes Town Forest in three different directions keeping an inventory of the species they identified. In addition, other volunteers unable to attend the event that day reported their findings from the week before and after the event. The result of these efforts is the species inventory list found in the right-hand column (verified 5/2011) of this report. The third column from the left contains observations made by Charles A. Moreno during the period of time he was working on the Forest Management Plan for the Glen Oakes Conservation Area (2009). Together the two columns represent the observed biodiversity of this area This conservation area, a part of the larger Spruce Swamp ecosystem, provides a unique haven of biodiversity. Much of the area inventoried has been identified as “highest quality habitat” or as important “supporting habitat” in the New Hampshire Wildlife Action Plan – please see the map printed on the cover of this report. It is worth noting the area contains the critical habitats required for several Species of Greatest Conservation Concern in New Hampshire. -
Native Plant List Trees.XLS
Lower Makefield Township Native Plant List* TREES LIGHT MOISTURE TYPE BOTANICAL NAME COMMON NAME STREET SUN PART SHADE DRY MOIST WET TREE SHADE EVERGREEN Chamaecyparis thyoides Atlantic White Cedar x x x x IIex opaca American Holly x x x x Juniperus virginiana Eastern Red Cedar x x x Picea glauca White Spruce x x x Picea pungens Blue Spruce x x x Pinus echinata Shortleaf Pine x x x Pinus resinosa Red Pine x x x Pinus rigida Pitch Pine x x Pinus strobus White Pine x x x Pinus virginiana Virginia Pine x x x Thuja occidentalis Eastern Arborvitae x x x x Tsuga canadensis Eastern Hemlock xx x DECIDUOUS Acer rubrum Red Maple x x x x x x Acer saccharinum Silver Maple x x x x Acer saccharum Sugar Maple x x x x Asimina triloba Paw-Paw x x Betula lenta Sweet Birch x x x x Betula nigra River Birch x x x x Betula populifolia Gray Birch x x x x x Carpinus caroliniana American Hornbeam x x x (C. tomentosa) Carya alba Mockernut Hickory x x x x Carya cordiformis Bitternut Hickory x x x Carya glabra Pignut Hickory x x x x x Carya ovata Shagbark Hickory x x Castanea pumila Allegheny Chinkapin xx x Celtis occidentalis Hackberry x x x x x x Crataegus crus-galli Cockspur Hawthorn x x x x Crataegus viridis Green Hawthorn x x x x Diospyros virginiana Common Persimmon x x x x Fagus grandifolia American Beech x x x x PAGE 1 Exhibit 1 TREES (cont'd) LIGHT MOISTURE TYPE BOTANICAL NAME COMMON NAME STREET SUN PART SHADE DRY MOIST WET TREE SHADE DECIDUOUS (cont'd) Fraxinus americana White Ash x x x x Fraxinus pennsylvanica Green Ash x x x x x Gleditsia triacanthos v. -
Jack Pine Department of Agriculture
Forest Service An American Wood United States Jack Pine Department of Agriculture FS-252 More than 99 percent of the jack pine growing in the United States is located in the Lake States, where it is one of the most important pulpwood species. Jack pine grows farther north into Canada than any other pine. It belongs to the hard pine group and is included as one of the important northeastern pines along with red pine and pitch pine. It can grow on dry sandy soils but grows best on well-drained loamy sands. The wood is moderately light and soft, moderately low in bending strength, and low in shock resistance. It is used primarily for pulpwood in the sulphate process, but it is also used for building construction, boxes, crates, shipping containers, posts, poles, pil- ing, mine timbers, railway ties, and fuel. An American Wood Jack Pine (Pinus banksiana Lamb.) Thomas D. Rudolph1 Distribution Jack pine grows in the northern forests of the United States and Canada (fig. 1). It grows farther into Canada than any other pine, with its northernmost extension reaching the Mackenzie River in the Northwest Territories. From there its northern limits extend eastward through Saskatchewan and Manitoba, Ontario and central Quebec, to Cape Breton Island, Nova Scotia. The southern edge of the range extends from Maine through central Michigan, northwest Indiana, and Wisconsin to Minnesota, then northwest through southern Manitoba, south-central Saskatchewan, and central Alberta to the extreme northeast of British Colum- bia. Isolated stands occur in southern Ontario, northern New York, and New Hampshire. -
Schall/Polloni Report to OPET 27 July 2014
Spring 2014 Rare Species and Habitat Investigations in the Woodlands and Wetlands of the WHOI parcels bordering Oyster Pond Environmental Trust’s Zinn Park Donald Schall and Pamela Polloni 27 July 2014 1.0 Introduction This Plant and Wildlife Habitat Assessment was prepared for Oyster Pond Environmental Trust in support of the acquisition of the property to protect important open space for Coastal Atlantic plant communities and resident and migratory bird species dependent on interior forest habitat. The presence of interior forest habitat for Neotropical migrants was demonstrated based on field observations completed during the spring 2014 migration period. Area sensitive interior forest species were recorded utilizing the woodland habitat in the avian surveys. In addition to the confirmation of avian use, our field surveys documented general wildlife use and confirmation of amphibian breeding activity in the pools of water in two isolated freshwater wetlands on the property. An inventory of higher vascular plants was also compiled to assess the diversity of plant species. 2.0 Woodland and Wetland Plant Communities The subject properties include both upland and wetland plant communities – Coastal Forest/Woodlands, Maple Swamp that includes portions dominated by Tupelo or Black Gum, a Shrub-dominated emergent wetland on a cove of the Oyster Pond shore, Shrub Swamps, and two Woodland Vernal Pools. Coastal Forest/Woodland (S3 priority habitat type in Massachusetts) is the dominant plant community on the largest parcel. The canopy includes a characteristic mixture of scarlet oak (Quercus coccinea), black oak (Q. velutina), and white oak (Q. alba), pitch pine (Pinus rigida), white pine (Pinus strobus), red maple (Acer rubrum), and American beech (Fagus grandifolia), with some pignut hickory (Carya glabra), eastern black cherry (Prunus serotina), tupelo (Nyssa sylvatica) and, eastern red cedar (Juniperus virginiana). -
Calvert County Native Plant List
February 2011 CALVERT COUNTY NATIVE PLANT LIST Canopy Trees (Generally > 35 ft. tall at maturity) Planting Stock: 2-in. caliper in size spaced 20-40 ft. on center Common Name Species Notes Box Elder Acer negundo Red Maple Acer rubrum Silver Maple Acer saccharinum River Birch Betula nigra Bitternut Hickory Carya cordiformis Pignut Hickory Carya glabra Shagbark Hickory Carya ovata Mockernut Hickory Carya tomentosa Common Hackberry Celtis occidentalis Atlantic White Cedar Chamaecyparis thyoides Evergreen Common Persimmon Diospyros virginiana American Beech Fagus grandifolia Black Walnut Juglans nigra Eastern Red Cedar Juniperus virginiana Evergreen Sweet Gum Liquidambar styraciflua Tulip Poplar Liriodendron tulipifera Red Mulberry Morus rubra Black Gum Nyssa sylvatica Salt Tolerant Shortleaf Pine Pinus echinata Evergreen Pitch Pine Pinus rigida Evergreen; Salt Tolerant Pond Pine Pinus serotina Evergreen Loblolly Pine Pinus taeda Evergreen Virginia Pine Pinus virgiana Evergreen American Sycamore Platanus occidentalis Black Cherry Prunus serotina Salt Tolerant White Oak Quercus alba Salt Tolerant Swamp White Oak Quercus bicolor Salt Tolerant Scarlet Oak Quercus coccinea Salt Tolerant Southern Red Oak Quercus falcata Blackjack Oak Quercus marilandica Swamp Chestnut Oak Quercus michauxii Chinquapin Oak Quercus muehlenbergii Water Oak Quercus nigra Pin Oak Quercus palustris Salt Tolerant Willow Oak Quercus phellos Chestnut Oak Quercus prinus Northern Red Oak Quercus rubra Salt Tolerant Post Oak Quercus stellata Salt Tolerant Black Oak Quercus velutina Salt Tolerant Black Locust Robinia pseudoacacia Bald Cypress Taxodium distichum Salt Tolerant American Basswood Tilia americana American Elm Ulmus americana 1 February 2011 CAL VERT COUNTY NATIVE PLANTS LIST (cont.) Understory Trees (Generally < 35 ft. tall at maturity) Planting Stock: 1 to 2-in. -
The Genetics of Shortleaf Pine (Pinus Echinata Mill.) with Implications for Restoration and Management
Tree Genetics & Genomes (2016) 12: 98 DOI 10.1007/s11295-016-1052-5 REVIEW The genetics of shortleaf pine (Pinus echinata mill.) with implications for restoration and management John F. Stewart1 & Rodney E. Will 2 & Barbara S. Crane3 & C. Dana Nelson4,5 Received: 5 January 2016 /Revised: 14 August 2016 /Accepted: 2 September 2016 /Published online: 17 September 2016 # Springer-Verlag Berlin Heidelberg 2016 Abstract Shortleaf pine (Pinus echinata Mill.) is an impor- prolific outcrosser, a trait it shares with other non-isolated mem- tant commercial timber resource and forest ecosystem compo- bers of the family Pinaceae. In recent years, however, it has nent in the southeastern USA. The species occurs in mainly shared less genetic material across long ranges, probably be- drier sites as an early- to mid-successional species, is fire- cause of habitat fragmentation. Various anthropogenic factors adapted, and it plays an important role in the fire ecology of also affect shortleaf pine’s future, as recent studies show that the region. However, shortleaf pine genetics are not well-stud- shortleaf pine introgression with loblolly pine puts the spe- ied, especially in this era of molecular genetics and genomics. cies—and the resiliency of southeastern forests—at risk. Most genetics research about the species has focused on prov- Importantly, fire exclusion is a likely cause of the increase in enance testing. Generally, shortleaf pine performs well in introgression. Herein, we provide further details and up-to-date colder areas, when compared to loblolly pine (Pinus taeda genetic information and resources for foresters and ecologists L.), a close relative, which is faster growing and the most interested in the restoration and management of shortleaf pine. -
Approved Plant List (PDF)
Harford County Approved Plant List April 2019 The Harford County Approved Plant list includes: Permitted tree and plant species for afforestation and reforestation, Permitted street tree species, and Permitted tree and plant species for individual landscaping Please note that not all of the plants on this list are native Maryland species, and therefore not all of the plant species on this list can be used to meet mitigation requirements within the Chesapeake Bay Critical Area. Please refer to the Native Plants list from US Fish and Wildlife, on Harford County’s website, for a comprehensive list of appropriate native plant species to use in the Critical Area. Harford County Approved Plant List April 2019 Plant Species Permitted for Afforestation and Reforestation Trees Scientific Name Common Name Acer negundo Boxelder Acer rubrum Red maple Acer saccharum Sugar maple Acer saccharinum Silver Maple Amelanchier canadensis Shadbush serviceberry Betula lenta Black or Sweet Gum Betula nigra River birch Carpinus caroliniana American hornbeam Carya cordiformis Bitternut hickory Carya glabra Pignut hickory Carya ovata Shagbark hickory Carya tomentosa Mockernut hickory Catalpa speciosa Northern catalpa Celtis occidentalis Common hackberry Cercis canadensis Eastern redbud Cornus florida Flowering dogwood Crataegus crus-galli Cockspur hawthorn Crataegus pruinosa Frosted hawthorn Crataegus punctata Dotted hawthorn Diospyros virginiana Common persimmon Fagus grandifolia American beech Hamamelis virginiana Common witchhazel Juglans cinerea Butternut -
Pinus Rigida (Pitch Pine) Grows from Quebec to Georgia Primarily in Mountains and Foothills
PinusPinus rigidarigida pitchpitch pinepine by Dr. Kim D. Coder, Professor of Tree Biology & Health Care Warnell School of Forestry & Natural Resources, University of Georgia Pinus rigida (pitch pine) grows from Quebec to Georgia primarily in mountains and foothills. Pinus rigida was first described as a species in 1768. The scientific name means a “pine with stiff cone scale.” The common name comes from early colonists use of Pinus rigida for producing turpentine and pitch for sailing vessels. The native range of Pinus rigida stretches from coastal and Eastern inland areas of Maine, South to Delaware, and then inland covering large portions of Southern 2/3s of Pennsylvania, West Virginia, Western Virginia, Southern Ohio, Eastern Kentucky, and the Tennessee / North Carolina border area. It grows into the far Northeast corner of Georgia. See the Georgia range map figure. It grows in Hardiness Zone 4a - 6b and Heat Zone 3-6. The lowest number of Hardiness Zone tends to delineate the Northern range limit and the largest Heat Zone number tends to define the South- ern edge of the range. This native Georgia pine grows in Coder Tree Grow Zone (CTGZ) A (a multiple climatic attribute based map), and in the temperature and precipitation cluster based Coder Tree Planting Zone 2. Figure 2. Pinus rigida grows on dry rocky slopes, lower ridge tops, and well drained slopes along middle elevations of the Appalachians mountains and their foot hills at the Southern end of its range. It has been found on swampy areas and floodplain areas in the Northern part of its range. -
American Forests 2020 National Register of Champion Trees
AMERICAN FORESTS 2020 NATIONAL REGISTER OF CHAMPION TREES Record Reference Number Year Nominated Nominated By Scientific Name Circumference (Inches) Height (Feet) Crown Spread (Feet) Total Points Year Last Verified Current Status Date Crowned County State 2915 1999 Steve Sillett and Robert Van Pelt Abies amabilis 212 222 38 444 2011 Champion 2012-03-23 Clallam WA 2907 1992 R.O. Brooks and C. Keeran Abies balsamea 160 104 53 277 2018 Champion 2019-09-13 Adams PA 3770 2006 Alan R. Washburn Abies bracteata 150 127 36 286 2016 Champion 2016-09-01 Monterey CA 5325 2013 Barbara Gardner Abies concolor 244 101 55.5 359 2013 Champion 2013-09-01 Utah UT 6582 2020 Carl Casey and Martin Crawford Abies concolor var. lowiana 229 227 42 467 2020 Co-Champion 2020-09-16 Mariposa CA 6581 2020 Carl Casey Abies concolor var. lowiana 236 220 46 468 2020 Co-Champion 2020-09-16 Mariposa CA 6361 2018 Carl Casey Abies concolor var. lowiana 261 201 37 471 2018 Co-Champion 2019-09-13 Tuolumne CA 6289 2018 Carl Casey, Martin Crawford, and Robert Van Pelt Abies concolor var. lowiana 259 199.5 48.5 471 2018 Co-Champion 2018-09-06 Mariposa CA 4638 2009 Byron Carmean, J. Murray, and Gary Williamson Abies fraseri 116 96 45 223 2012 Champion 2012-09-01 Harrisonburg VA 5250 2013 Robert Van Pelt Abies grandis 265 227 48 504 2018 Co-Champion 2019-11-12 Clallam WA 2912 1997 Dale Thornburg and Robert Van Pelt Abies grandis 245 257 36 511 2015 Co-Champion 2015-09-01 Humboldt CA 2917 1965 Stephen Arno and Oscar Sedergren Abies lasiocarpa 252 125 26 384 2015 Champion 2015-09-01 Jefferson WA 2908 1999 R. -
App B APB Pine Barrens Viability Assessment
Appendix B. Albany Pine Bush Pine Barrens Viability Assessment Albany Pine Bush Pine Barrens Viability Assessment Quantifiable indicators of pine barrens size and extent, fragmentation and edge effects, prescribed fire regime, and biotic patterns Prepared for: Albany Pine Bush Preserve Commission Prepared by: Jason Bried Preserve Ecologist And Neil Gifford Conservation Director November 2008 Albany Pine Bush Pine Barrens Viability Assessment November 2008 Table of Contents Acknowledgements ........................................................................................................... 3 I. INTRODUCTION ......................................................................................................... 4 Planning & Conservation Target .......................................................................... 4 Albany Pine Bush .................................................................................................. 6 Coarse vs. Fine Filter Monitoring ........................................................................ 8 Assessment Framework ......................................................................................... 8 Literature Cited................................................................................................................. 12 II. Size & Extent .............................................................................................................. 17 Habitat amount .................................................................................................... 18