Early Successional Habitat
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Lepidoptera of North America 5
Lepidoptera of North America 5. Contributions to the Knowledge of Southern West Virginia Lepidoptera Contributions of the C.P. Gillette Museum of Arthropod Diversity Colorado State University Lepidoptera of North America 5. Contributions to the Knowledge of Southern West Virginia Lepidoptera by Valerio Albu, 1411 E. Sweetbriar Drive Fresno, CA 93720 and Eric Metzler, 1241 Kildale Square North Columbus, OH 43229 April 30, 2004 Contributions of the C.P. Gillette Museum of Arthropod Diversity Colorado State University Cover illustration: Blueberry Sphinx (Paonias astylus (Drury)], an eastern endemic. Photo by Valeriu Albu. ISBN 1084-8819 This publication and others in the series may be ordered from the C.P. Gillette Museum of Arthropod Diversity, Department of Bioagricultural Sciences and Pest Management Colorado State University, Fort Collins, CO 80523 Abstract A list of 1531 species ofLepidoptera is presented, collected over 15 years (1988 to 2002), in eleven southern West Virginia counties. A variety of collecting methods was used, including netting, light attracting, light trapping and pheromone trapping. The specimens were identified by the currently available pictorial sources and determination keys. Many were also sent to specialists for confirmation or identification. The majority of the data was from Kanawha County, reflecting the area of more intensive sampling effort by the senior author. This imbalance of data between Kanawha County and other counties should even out with further sampling of the area. Key Words: Appalachian Mountains, -
Effects of Prescribed Fire and Fire Surrogates on Pollinators and Saproxylic Beetles in North Carolina and Alabama
EFFECTS OF PRESCRIBED FIRE AND FIRE SURROGATES ON POLLINATORS AND SAPROXYLIC BEETLES IN NORTH CAROLINA AND ALABAMA by JOSHUA W. CAMPBELL (Under the Direction of James L. Hanula) ABSTRACT Pollinating and saproxylic insects are two groups of forest insects that are considered to be extremely vital for forest health. These insects maintain and enhance plant diversity, but also help recycle nutrients back into the soil. Forest management practices (prescribed burns, thinnings, herbicide use) are commonly used methods to limit fuel build up within forests. However, their effects on pollinating and saproxylic insects are poorly understood. We collected pollinating and saproxylic insect from North Carolina and Alabama from 2002-2004 among different treatment plots. In North Carolina, we captured 7921 floral visitors from four orders and 21 families. Hymenoptera was the most abundant and diverse order, with Halictidae being the most abundant family. The majority of floral visitors were captured in the mechanical plus burn treatments, while lower numbers were caught on the mechanical only treatments, burn only treatments and control treatments. Overall species richness was also higher on mechanical plus burn treatments compared to other treatments. Total pollinator abundance was correlated with decreased tree basal area (r2=0.58) and increased percent herbaceous plant cover (r2=0.71). We captured 37,191 saproxylic Coleoptera in North Carolina, comprising 20 families and 122 species. Overall, species richness and total abundance of Coleoptera were not significantly different among treatments. However, total numbers of many key families, such as Scolytidae, Curculionidae, Cerambycidae, and Buprestidae, have higher total numbers in treated plots compared to untreated controls and several families (Elateridae, Cleridae, Trogositidae, Scolytidae) showed significant differences (p≤0.05) in abundance. -
Insect Survey of Four Longleaf Pine Preserves
A SURVEY OF THE MOTHS, BUTTERFLIES, AND GRASSHOPPERS OF FOUR NATURE CONSERVANCY PRESERVES IN SOUTHEASTERN NORTH CAROLINA Stephen P. Hall and Dale F. Schweitzer November 15, 1993 ABSTRACT Moths, butterflies, and grasshoppers were surveyed within four longleaf pine preserves owned by the North Carolina Nature Conservancy during the growing season of 1991 and 1992. Over 7,000 specimens (either collected or seen in the field) were identified, representing 512 different species and 28 families. Forty-one of these we consider to be distinctive of the two fire- maintained communities principally under investigation, the longleaf pine savannas and flatwoods. An additional 14 species we consider distinctive of the pocosins that occur in close association with the savannas and flatwoods. Twenty nine species appear to be rare enough to be included on the list of elements monitored by the North Carolina Natural Heritage Program (eight others in this category have been reported from one of these sites, the Green Swamp, but were not observed in this study). Two of the moths collected, Spartiniphaga carterae and Agrotis buchholzi, are currently candidates for federal listing as Threatened or Endangered species. Another species, Hemipachnobia s. subporphyrea, appears to be endemic to North Carolina and should also be considered for federal candidate status. With few exceptions, even the species that seem to be most closely associated with savannas and flatwoods show few direct defenses against fire, the primary force responsible for maintaining these communities. Instead, the majority of these insects probably survive within this region due to their ability to rapidly re-colonize recently burned areas from small, well-dispersed refugia. -
Intermediate Disturbance Hypothesis
TIEE Teaching Issues and Experiments in Ecology - Volume 1, January 2004 ISSUES – FIGURE SET Ecology of Disturbance Charlene D'Avanzo, School of Natural Sciences Hampshire College, Amherst, MA, 01002 [email protected] Controlled fire, © Konza Prairie LTER, Manhattan, KS {www.konza.ksu.edu/ gallery/hulbert.jpg} Figure Set 1: Intermediate Disturbance Hypothesis Purpose: To illustrate the intermediate disturbance hypothesis with 2 field experiments. Teaching Approach: "Pairs Share" Cognitive Skills: (see Bloom's Taxonomy) — comprehension, interpretation, application, analysis Student Assessment: Take home or in class essay quiz © 2004 – Charlene D’Avanzo and the Ecological Society of America. Teaching Issues and Experiments in Ecology, TIEE Volume 1 © 2004 - Ecological Society of America (www.tiee.ecoed.net). page 2 Charlene D’Avanzo TIEE Volume 1, January 2004 BACKGROUND W. Sousa (1979) In this study, Wayne Sousa tested the intermediate disturbance hypothesis proposed by Connell (1978). In the 70's and 80's ecologists hotly debated factors explaining high diversity in tropical regions and bottom of the deep sea. Popular ideas included: the time hypothesis (older communities are more diverse), the competition hypothesis (in agreeable climates where biological and not physical factors prevail, interspecific competition and niche partitioning results in high diversity), and the environmental stability hypothesis (relatively unchanging physical variables allow more species to exist). Connell questioned all of these and reasoned instead that highest species diversity exists under conditions of intermediate disturbance. He proposed that in recently disturbed communities a few early colonizing species prevail; similarly after a long time diversity is also low, but these few are long-living and competitively dominant organisms. -
Behr's Hairstreak (Satyrium Behrii)
PROPOSED Species at Risk Act Recovery Strategy Series Adopted under Section 44 of SARA Recovery Strategy for the Behr’s Hairstreak (Satyrium behrii) in Canada Behr’s Hairstreak 2014 Recommended citation: Environment Canada. 2014. Recovery Strategy for the Behr’s Hairstreak (Satyrium behrii) in Canada [Proposed]. Species at Risk Act Recovery Strategy Series. Environment Canada, Ottawa. 26 pp. + Appendix. For copies of the recovery strategy, or for additional information on species at risk, including the Committee on the Status of Endangered Wildlife in Canada (COSEWIC) Status Reports, residence descriptions, action plans, and other related recovery documents, please visit the Species at Risk (SAR) Public Registry. Cover illustration: Neil K. Dawe Également disponible en français sous le titre « Programme de rétablissement du porte-queue de Behr (Satyrium behrii) au Canada [Proposition] » © Her Majesty the Queen in Right of Canada, represented by the Minister of the Environment, 2014. All rights reserved. ISBN Catalogue no. Content (excluding the illustrations) may be used without permission, with appropriate credit to the source. RECOVERY STRATEGY FOR THE BEHR’S HAIRSTREAK (Satyrium behrii) IN CANADA 2014 Under the Accord for the Protection of Species at Risk (1996), the federal, provincial, and territorial governments agreed to work together on legislation, programs, and policies to protect wildlife species at risk throughout Canada. In the spirit of cooperation of the Accord, the Government of British Columbia has given permission to the Government of Canada to adopt the “Recovery Strategy for Behr’s Hairstreak (Satyrium behrii) in British Columbia” (Part 2) under Section 44 of the Species at Risk Act (SARA). -
Chapter 5 Species Interactions, Ecological Succession, and Population Control How Do Species Interact?
Chapter 5 Species interactions, Ecological Succession, and Population Control How do species interact? Give some limited resources that organisms need in order to survive. Food, shelter, space, mate to reproduce, water, light air How might species interact to get these limited resources? Competition Have you ever competed with another organism to get what you wanted/needed? Interspecific competition is between different species. Intraspecific competition is between a single species. Competition Species need to compete because their niches overlap and they end up sharing the limited resources. When the word “share” is used here, it doesn’t mean equal sharing. Species like to reduce or avoid competition, so they resource partition. Competition Resource partitioning is a way for organisms to share a resource by using the resource at different times or using different parts of the resource. Predator/Prey interactions Predator is the hunter and feeds on the prey (the hunted) This interaction has a strong effect on population sizes. Predator/Prey interactions pg 134- 135 Give a way predators capture their prey. What are some ways prey avoid predators? Birds of prey (predators) and prey Google search ‘Birds of Prey’ – the Nature Conservancy has a great site Google search ‘bluebird, robin, sparrow’ Answer: 1. What differences do you notice regarding placement of the eyes in each group? 2. How might the difference in eye placement benefit each group of birds? What is mimicry? • Mimicry is the similarity of one species to another species which protects one or both organisms. Can be in appearance, behavior, sound, scent and even location. Who are the players? Mimics can be good tasting (easy targets) so they need to gain protection by looking like something bad tasting or dangerous. -
CBD First National Report
FIRST NATIONAL REPORT OF THE REPUBLIC OF SERBIA TO THE UNITED NATIONS CONVENTION ON BIOLOGICAL DIVERSITY July 2010 ACRONYMS AND ABBREVIATIONS .................................................................................... 3 1. EXECUTIVE SUMMARY ........................................................................................... 4 2. INTRODUCTION ....................................................................................................... 5 2.1 Geographic Profile .......................................................................................... 5 2.2 Climate Profile ...................................................................................................... 5 2.3 Population Profile ................................................................................................. 7 2.4 Economic Profile .................................................................................................. 7 3 THE BIODIVERSITY OF SERBIA .............................................................................. 8 3.1 Overview......................................................................................................... 8 3.2 Ecosystem and Habitat Diversity .................................................................... 8 3.3 Species Diversity ............................................................................................ 9 3.4 Genetic Diversity ............................................................................................. 9 3.5 Protected Areas .............................................................................................10 -
Mechanism of Ecological Succession
Environmental Biology Prof.(Dr.) Punam Jeswal Head M.Sc semester IV Botany Department MECHANISM OF ECOLOGICAL SUCCESSION ECOLOGICAL SUCCESSION Ecological succession is the gradual and continuous change in the species composition and community structure over time in the same area. Environment is always kept on changing over a period of time due to - i) Variations in climatic and physiographic factors and ii) The activities of the species of the communities themselves. These influences bring changes in the existing community which is sooner or later replaced by another community developed one after another. This process continues and successive communities develop one after another over the same area, until the terminal final community again becomes more or less stable for a period of time. The occurrence of definite sequence of communities over a period of time in the same area is known as Ecological Succession. Succession is a unidirectional progressive series of changes which leads to the established of a relatively stable community. Hult (1885), while studying communities of Southern Sweden used for the first time the term succession for the orderly changes in the communities. Clements (1907, 1916) put forth various principles that governed the process of succession, and while studying plant communities, defined succession as ' the natural process by which the same locality becomes successively colonized by different groups or communities of plants. According to E.P. Odum (1971), the ecological succession is an orderly process of community change in a unity area. It is the process of changes in species composition in an ecosystem over time. In simple terms, it is the process of ecosystem development in nature. -
Is Ecological Succession Predictable?
Is ecological succession predictable? Commissioned by Prof. dr. P. Opdam; Kennisbasis Thema 1. Project Ecosystem Predictability, Projectnr. 232317. 2 Alterra-Report 1277 Is ecological succession predictable? Theory and applications Koen Kramer Bert Brinkman Loek Kuiters Piet Verdonschot Alterra-Report 1277 Alterra, Wageningen, 2005 ABSTRACT Koen Kramer, Bert Brinkman, Loek Kuiters, Piet Verdonschot, 2005. Is ecological succession predictable? Theory and applications. Wageningen, Alterra, Alterra-Report 1277. 80 blz.; 6 figs.; 0 tables.; 197 refs. A literature study is presented on the predictability of ecological succession. Both equilibrium and nonequilibrium theories are discussed in relation to competition between, and co-existence of species. The consequences for conservation management are outlined and a research agenda is proposed focusing on a nonequilibrium view of ecosystem functioning. Applications are presented for freshwater-; marine-; dune- and forest ecosystems. Keywords: conservation management; competition; species co-existence; disturbance; ecological succession; equilibrium; nonequilibrium ISSN 1566-7197 This report can be ordered by paying € 15,- to bank account number 36 70 54 612 by name of Alterra Wageningen, IBAN number NL 83 RABO 036 70 54 612, Swift number RABO2u nl. Please refer to Alterra-Report 1277. This amount is including tax (where applicable) and handling costs. © 2005 Alterra P.O. Box 47; 6700 AA Wageningen; The Netherlands Phone: + 31 317 474700; fax: +31 317 419000; e-mail: [email protected] No part of this publication may be reproduced or published in any form or by any means, or stored in a database or retrieval system without the written permission of Alterra. Alterra assumes no liability for any losses resulting from the use of the research results or recommendations in this report. -
How to Use This Checklist
How To Use This Checklist Swallowtails: Family Papilionidae Special Note: Spring and Summer Azures have recently The information presented in this checklist reflects our __ Pipevine Swallowtail Battus philenor R; May - Sep. been recognized as separate species. Azure taxonomy has not current understanding of the butterflies found within __ Zebra Swallowtail Eurytides marcellus R; May - Aug. been completely sorted out by the experts. Cleveland Metroparks. (This list includes all species that have __ Black Swallowtail Papilio polyxenes C; May - Sep. __ Appalachian Azure Celastrina neglecta-major h; mid - late been recorded in Cuyahoga County, and a few additional __ Giant Swallowtail Papilio cresphontes h; rare in Cleveland May; not recorded in Cuy. Co. species that may occur here.) Record you observations and area; July - Aug. Brush-footed Butterflies: Family Nymphalidae contact a naturalist if you find something that may be of __ Eastern Tiger Swallowtail Papilio glaucus C; May - Oct.; __ American Snout Libytheana carinenta R; June - Oct. interest. females occur as yellow or dark morphs __ Variegated Fritillary Euptoieta claudia R; June - Oct. __ Spicebush Swallowtail Papilio troilus C; May - Oct. __ Great Spangled Fritillary Speyeria cybele C; May - Oct. Species are listed taxonomically, with a common name, a Whites and Sulphurs: Family Pieridae __ Aphrodite Fritillary Speyeria aphrodite O; June - Sep. scientific name, a note about its relative abundance and flight __ Checkered White Pontia protodice h; rare in Cleveland area; __ Regal Fritillary Speyeria idalia X; no recent Ohio records; period. Check off species that you identify within Cleveland May - Oct. formerly in Cleveland Metroparks Metroparks. __ West Virginia White Pieris virginiensis O; late Apr. -
Specimen Records for North American Lepidoptera (Insecta) in the Oregon State Arthropod Collection. Lycaenidae Leach, 1815 and Riodinidae Grote, 1895
Catalog: Oregon State Arthropod Collection 2019 Vol 3(2) Specimen records for North American Lepidoptera (Insecta) in the Oregon State Arthropod Collection. Lycaenidae Leach, 1815 and Riodinidae Grote, 1895 Jon H. Shepard Paul C. Hammond Christopher J. Marshall Oregon State Arthropod Collection, Department of Integrative Biology, Oregon State University, Corvallis OR 97331 Cite this work, including the attached dataset, as: Shepard, J. S, P. C. Hammond, C. J. Marshall. 2019. Specimen records for North American Lepidoptera (Insecta) in the Oregon State Arthropod Collection. Lycaenidae Leach, 1815 and Riodinidae Grote, 1895. Catalog: Oregon State Arthropod Collection 3(2). (beta version). http://dx.doi.org/10.5399/osu/cat_osac.3.2.4594 Introduction These records were generated using funds from the LepNet project (Seltmann) - a national effort to create digital records for North American Lepidoptera. The dataset published herein contains the label data for all North American specimens of Lycaenidae and Riodinidae residing at the Oregon State Arthropod Collection as of March 2019. A beta version of these data records will be made available on the OSAC server (http://osac.oregonstate.edu/IPT) at the time of this publication. The beta version will be replaced in the near future with an official release (version 1.0), which will be archived as a supplemental file to this paper. Methods Basic digitization protocols and metadata standards can be found in (Shepard et al. 2018). Identifications were confirmed by Jon Shepard and Paul Hammond prior to digitization. Nomenclature follows that of (Pelham 2008). Results The holdings in these two families are extensive. Combined, they make up 25,743 specimens (24,598 Lycanidae and 1145 Riodinidae). -
Upper Saco River Focus Areas of Statewide Ecological Significance Upper Saco River
Focus Areas of Statewide Ecological Significance: Upper Saco River Focus Areas of Statewide Ecological Significance Upper Saco River Biophysical Region • Sebago - Ossipee Hills and Plain WHY IS THIS AREA SIGNIFICANT? Rare Animals The Upper Saco River Focus Area is one of the most Comet Darner Extra-striped Snaketail Lilypad Clubtail Spatterdock Darner biodiverse areas in Maine. It is home to numerous Buckmoth Southern Pygmy Clubtail rare species and natural communities, including Sedge Wren Huckleberry Sphinx one of the largest concentrations of the globally Wood Turtle Common Sanddragon rare Long’s bulrush (Scirpus longii), three globally Rapids Clubtail Edwards’ Hairstreak Cobra Clubtail Common Musk Turtle rare dragonfly species, the globally rare river- Barrens Itame Eastern Ribbon Snake wash barrens community, outstanding examples Twilight Moth Ebony Boghaunter of floodplain forests, and at least ten other plant Boreal Snaketail Ringed Boghaunter species that are rare in Maine. Rare animals in the Pygmy Snaketail Similar Underwing New England Bluet Acadian Swordgrass Moth Focus Area represent diverse taxonomic groups, Pine Barrens Zanclognatha such as birds, reptiles, odonates, and lepidopterans. Rare Plants Secund Rush Adder’s Tongue Fern OPPORTUNITIES FOR CONSERVATION Mountain-laurel Smooth Sandwort Dwarf Bulrush Douglas’ Knotweed » Work with willing landowners to permanently Silverling Blunt-lobed Woodsia protect remaining undeveloped areas. Fall Fimbry Fern-leaved False Foxglove » Educate recreational users about ecological and