Comparison of Swamp Forest and Phragmites Australis
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Brodhead Watershed Conservation Plan
Brodhead Watershed Conservation Plan January, 2002 Prepared by: Brodhead Watershed Association With: BLOSS Associates Brodhead Watershed Conservation Plan Acknowledgements The Watershed Partners were the backbone of this planning process. Their commitment to preserving and protecting the watershed underlies this entire plan. Watershed Partners / Conservation Plan Steering Committee Monroe County Commissioners – Mario Scavello, Donna Asure, James Cadue, Former Commissioner Janet Weidensaul Monroe County Conservation District – Craig Todd, Darryl Speicher Monroe County Planning Commission – John Woodling, Eric Bartolacci Monroe County Historical Association – Candace McGreevey Monroe County Office of Emergency Management – Harry Robidoux Monroe County Open Space Advisory Board – Tom O’Keefe Monroe County Recreation & Park Commission – Kara Derry Monroe 2020 Executive Committee – Charles Vogt PA Department of Environmental Protection – Bill Manner Pennsylvania State University – Jay Stauffer Penn State Cooperative Extension – Peter Wulfhurst Stroudsburg Municipal Authority – Ken Brown Mount Pocono Borough – Nancy Golowich Pocono/Hamilton/Jackson Open Space Committee – Cherie Morris Stroud Township – Ross Ruschman, Ed Cramer Smithfield Township – John Yetter Delaware River Basin Commission – Pamela V’Combe, Carol Collier U.S. Environmental Protection Agency – Susan McDowell Delaware Water Gap National Recreation Area – Denise Cook National Park Service, Rivers & Trails Office – David Lange National Institute for Environmental Renewal (no longer -
Evaluation of Approaches for Mapping Tidal Wetlands of the Chesapeake and Delaware Bays
remote sensing Article Evaluation of Approaches for Mapping Tidal Wetlands of the Chesapeake and Delaware Bays Brian T. Lamb 1,2,* , Maria A. Tzortziou 1,3 and Kyle C. McDonald 1,2,4 1 Department of Earth and Atmospheric Sciences, The City College of New York, City University of New York, New York, NY 10031, USA; [email protected] (M.A.T.); [email protected] (K.C.M.) 2 Earth and Environmental Sciences Program, The Graduate Center, City University of New York, New York, NY 10016, USA 3 NASA Goddard Space Flight Center, Greenbelt, MD 20771, USA 4 Carbon Cycle and Ecosystems Group, Jet Propulsion Laboratory, California Institute of Technology, Pasadena, CA 91109, USA * Correspondence: [email protected] Received: 1 July 2019; Accepted: 3 October 2019; Published: 12 October 2019 Abstract: The spatial extent and vegetation characteristics of tidal wetlands and their change are among the biggest unknowns and largest sources of uncertainty in modeling ecosystem processes and services at the land-ocean interface. Using a combination of moderate-high spatial resolution ( 30 meters) optical and synthetic aperture radar (SAR) satellite imagery, we evaluated several ≤ approaches for mapping and characterization of wetlands of the Chesapeake and Delaware Bays. Sentinel-1A, Phased Array type L-band Synthetic Aperture Radar (PALSAR), PALSAR-2, Sentinel-2A, and Landsat 8 imagery were used to map wetlands, with an emphasis on mapping tidal marshes, inundation extents, and functional vegetation classes (persistent vs. non-persistent). We performed initial characterizations at three target wetlands study sites with distinct geomorphologies, hydrologic characteristics, and vegetation communities. -
Alternative Stable States of Tidal Marsh Vegetation Patterns and Channel Complexity
ECOHYDROLOGY Ecohydrol. (2016) Published online in Wiley Online Library (wileyonlinelibrary.com) DOI: 10.1002/eco.1755 Alternative stable states of tidal marsh vegetation patterns and channel complexity K. B. Moffett1* and S. M. Gorelick2 1 School of the Environment, Washington State University Vancouver, Vancouver, WA, USA 2 Department of Earth System Science, Stanford University, Stanford, CA, USA ABSTRACT Intertidal marshes develop between uplands and mudflats, and develop vegetation zonation, via biogeomorphic feedbacks. Is the spatial configuration of vegetation and channels also biogeomorphically organized at the intermediate, marsh-scale? We used high-resolution aerial photographs and a decision-tree procedure to categorize marsh vegetation patterns and channel geometries for 113 tidal marshes in San Francisco Bay estuary and assessed these patterns’ relations to site characteristics. Interpretation was further informed by generalized linear mixed models using pattern-quantifying metrics from object-based image analysis to predict vegetation and channel pattern complexity. Vegetation pattern complexity was significantly related to marsh salinity but independent of marsh age and elevation. Channel complexity was significantly related to marsh age but independent of salinity and elevation. Vegetation pattern complexity and channel complexity were significantly related, forming two prevalent biogeomorphic states: complex versus simple vegetation-and-channel configurations. That this correspondence held across marsh ages (decades to millennia) -
Common Reed Phragmites Australis (Cav.) Trin. Ex Steud. Grass Family (Poaceae)
FACT SHEET: GIANT REED Common Reed Phragmites australis (Cav.) Trin. ex Steud. Grass family (Poaceae) NATIVE RANGE Eurasia DESCRIPTION Common reed, or Phragmites, is a tall, perennial grass that can grow to over 15 feet in height. In North America, both native phragmites (Phragmites australis ssp. americanus Saltonstall, P.M. Peterson & Soreng) and introduced subspecies are found. Introduced Phragmites forms dense stands which include both live stems and standing dead stems from previous year’s growth. Leaves are elongate and typically 1-1.5 inches wide at their widest point. Flowers form bushy panicles in late July and August and are usually purple or golden in color. As seeds mature, the panicles begin to look “fluffy” due to the hairs on the seeds and they take on a grey sheen. Below ground, Phragmites forms a dense network of roots and rhizomes which can go down several feet in depth. The plant spreads horizontally by sending out rhizome runners which can grow 10 or more feet in a single growing season if conditions are optimal. Please see the table below for information on distinguishing betweeen native and introduced Phragmites. ECOLOGICAL THREAT Once introduced Phragmites invades a site it quickly can take over a marsh community, crowding out native plants, changing marsh hydrology, altering wildlife habitat, and increasing fire potential. Its high biomass blocks light to other plants and occupies all the growing space belowground so plant communities can turn into a Phragmites monoculture very quickly. Phragmites can spread both by seed dispersal and by vegetative spread via fragments of rhizomes that break off and are transported elsewhere. -
Draft Wetland Mapping Standard
FGDC Working Draft Wetland Mapping Standard FGDC Wetland Subcommittee and Wetland Mapping Standard Workgroup Submitted by: Margarete Heber Environmental Protection Agency Office of Water Date: March 26, 2007 Federal Geographic Data Committee Wetland Mapping Standard Table of Contents 1 Introduction................................................................................................................. 1 1.1 Background.......................................................................................................... 1 1.2 Objective.............................................................................................................. 1 1.3 Scope.................................................................................................................... 2 1.4 Applicability ........................................................................................................ 4 1.5 FGDC Standards and Other Related Practices..................................................... 4 1.6 Standard Development Procedures and Representation ...................................... 5 1.7 Maintenance Authority ........................................................................................ 5 2 FGDC requirements and Quality components............................................................ 6 2.1 Source Imagery .................................................................................................... 6 2.2 Classification....................................................................................................... -
NATIONAL WETLANDS INVENTORY and the NATIONAL WETLANDS RESEARCH CENTER PROJECT REPORT FOR: GALVESTON BAY INTRODUCTION the U.S. Fi
NATIONAL WETLANDS INVENTORY AND THE NATIONAL WETLANDS RESEARCH CENTER PROJECT REPORT FOR: GALVESTON BAY INTRODUCTION The U.S. Fish & Wildlife Service's National Wetlands Inventory is producing maps showing the location and classification of wetlands and deepwater habitats of the United States. The Classification of Wetlands and Deepwater Habitats of the United States by Cowardin et al. is the classification system used to define and classify wetlands. Upland classification will utilize the system put forth in., A Land Use and Land Cover Classification System For Use With Remote Sensor Data. by James R. Anderson, Ernest E. Hardy, John T. Roach, and Richard E. Witmer. Photo interpretation conventions, hydric soils-lists and wetland plants lists are also available to enhance the use and application of the classification system. The purpose of the report to users is threefold: (1) to provide localized information regarding the production of NWI maps, including field reconnaissance with a discussion of imagery and interpretation; (2) to provide a descriptive crosswalk from wetland codes on the map to common names and representative plant species; and (3) to explain local geography, climate, and wetland communities. II. FIELD RECONNAISSANCE Field reconnaissance of the work area is an integral part for the accurate interpretation of aerial photography. Photographic signatures are compared to the wetland's appearance in the field by observing vegetation, soil and topography. Thus information is weighted for seasonality and conditions existing at the time of photography and at ground truthing. Project Area The project area is located in the southeastern portion of Texas along the coast. Ground truthing covered specific quadrangles of each 1:100,000 including Houston NE, Houston SE, Houston NW, and Houston SW (See Appendix A, Locator Map). -
Appendix B Wells Harbor Ecology (Materials from the Wells NERR)
APPENDICES Appendix B Wells Harbor Ecology (materials from the Wells NERR) CHAPTER 8 Vegetation Caitlin Mullan Crain lants are primary producers that use photosynthesis ter). In this chapter, we will describe what these vegeta- to convert light energy into carbon. Plants thus form tive communities look like, special plant adaptations for Pthe base of all food webs and provide essential nutrition living in coastal habitats, and important services these to animals. In coastal “biogenic” habitats, the vegetation vegetative communities perform. We will then review also engineers the environment, and actually creates important research conducted in or affiliated with Wells the habitat on which other organisms depend. This is NERR on the various vegetative community types, giving particularly apparent in coastal marshes where the plants a unique view of what is known about coastal vegetative themselves, by trapping sediments and binding the communities of southern Maine. sediment with their roots, create the peat base and above- ground structure that defines the salt marsh. The plants OASTAL EGETATION thus function as foundation species, dominant C V organisms that modify the physical environ- Macroalgae ment and create habitat for numerous dependent Algae, commonly known as seaweeds, are a group of organisms. Other vegetation types in coastal non-vascular plants that depend on water for nutrient systems function in similar ways, particularly acquisition, physical support, and seagrass beds or dune plants. Vegetation is reproduction. Algae are therefore therefore important for numerous reasons restricted to living in environ- including transforming energy to food ments that are at least occasionally sources, increasing biodiversity, and inundated by water. -
Marsh-Pond-Marsh Constructed Wetland Design Analysis for Swine Lagoon Wastewater Treatment
Ecological Engineering 23 (2004) 127–133 Marsh-pond-marsh constructed wetland design analysis for swine lagoon wastewater treatment K.C. Stonea,∗, M.E. Poacha, P.G. Hunta, G.B. Reddyb a USDA-ARS, 2611 West Lucas Street, Florence, SC 29501, USA b North Carolina A&T State University, Greensboro, NC, USA. Received 29 March 2004; received in revised form 23 July 2004; accepted 26 July 2004 Abstract Constructed wetlands have been identified as a potentially important component of animal wastewater treatment systems. Continuous marsh constructed wetlands have been shown to be effective in treating swine lagoon effluent and reducing the land needed for terminal application. Constructed wetlands have also been used widely in polishing wastewater from municipal systems. Constructed wetland design for animal wastewater treatment has largely been based on that of municipal systems. The objective of this research was to determine if a marsh-pond-marsh wetland system could be described using existing design approaches used for constructed wetland design. The marsh-pond-marsh wetlands investigated in this study were constructed in 1995 at the North Carolina A&T University research farm near Greensboro, NC. There were six wetland systems (11 m × 40 m). The first 10-m was a marsh followed by a 20-m pond section followed by a 10-m marsh planted with bulrushes and cattails. The wetlands were effective in treating nitrogen with mean total nitrogen and ammonia-N concentration reductions of approximately 30%; however, they were not as effective in the treatment of phosphorus (8%). Outflow concentrations were reasonably correlated (r2 ≥ 0.86 and r2 ≥ 0.83, respectively) to inflow concentrations and hydraulic loading rates for both total N and ammonia-N. -
Exploring Our Wonderful Wetlands Publication
Exploring Our Wonderful Wetlands Student Publication Grades 4–7 Dear Wetland Students: Are you ready to explore our wonderful wetlands? We hope so! To help you learn about several types of wetlands in our area, we are taking you on a series of explorations. As you move through the publication, be sure to test your wetland wit and write about wetlands before moving on to the next exploration. By exploring our wonderful wetlands, we hope that you will appreciate where you live and encourage others to help protect our precious natural resources. Let’s begin our exploration now! Southwest Florida Water Management District Exploring Our Wonderful Wetlands Exploration 1 Wading Into Our Wetlands ................................................Page 3 Exploration 2 Searching Our Saltwater Wetlands .................................Page 5 Exploration 3 Finding Out About Our Freshwater Wetlands .............Page 7 Exploration 4 Discovering What Wetlands Do .................................... Page 10 Exploration 5 Becoming Protectors of Our Wetlands ........................Page 14 Wetlands Activities .............................................................Page 17 Websites ................................................................................Page 20 Visit the Southwest Florida Water Management District’s website at WaterMatters.org. Exploration 1 Wading Into Our Wetlands What exactly is a wetland? The scientific and legal definitions of wetlands differ. In 1984, when the Florida Legislature passed a Wetlands Protection Act, they decided to use a plant list containing plants usually found in wetlands. We are very fortunate to have a lot of wetlands in Florida. In fact, Florida has the third largest wetland acreage in the United States. The term wetlands includes a wide variety of aquatic habitats. Wetland ecosystems include swamps, marshes, wet meadows, bogs and fens. Essentially, wetlands are transitional areas between dry uplands and aquatic systems such as lakes, rivers or oceans. -
Ecology and Management of Arundo Donax, and Approaches to Riparian Habitat Restoration in Southern California
ECOLOGY AND MANAGEMENT OF ARUNDO DONAX, AND APPROACHES TO RIPARIAN HABITAT RESTORATION IN SOUTHERN CALIFORNIA. Gary P. Bell The Nature Conservancy of New Mexico, 212 E. Marcy Street, Suite 200, Santa Fe, NM 87501 USA Abstract By far the greatest threat to the dwindling riparian resources of coastal southern California is the alien grass species known as Arundo donax. Over the last 25 years the riparian forests of coastal southern California have become infested with A. donax which has spread by flood-fragmentation and dispersal of vegetative propagules. Arundo donax dramatically alters the ecological/successional processes in riparian systems and ultimately moves most riparian habitats towards pure stands of this alien grass. By current estimates there are tens of thousands of acres of A. donax along the major coastal drainage systems of southern California, including the Santa Ana, Santa Margarita, Ventura, Santa Clara, San Diego, and San Luis Rey rivers. The removal of A. donax from these systems provides numerous downstream benefits in terms of native species habitat, wildfire protection, water quantity and water quality. Introduction Arundo L. is a genus of tall perennial reed-like grasses (Poaceae) with six species native to warmer parts of the Old World. Arundo donax L. (giant reed, bamboo reed, giant reed grass, arundo grass, donax cane, giant cane, river cane, bamboo cane, canne de Provence), is the largest member of the genus and is among the largest of the grasses, growing to a height of 8 m (Fig. 1). This species is believed to be native to freshwaters of eastern Asia (Polunin and Huxley 1987), but has been cultivated throughout Asia, southern Europe, north Africa, and the Middle East for thousands of years and has been planted widely in North and South America and Australasia in the past century (Perdue 1958, Zohary 1962). -
MANAGING the TOP FIVE INVASIVE PLANTS in CALVERT COUNTY 1. What Are the Top 5 Invasive Plants in Calvert County? Phragmites
MANAGING THE TOP FIVE INVASIVE PLANTS IN CALVERT COUNTY 1. What are the top 5 invasive plants in Calvert County? Phragmites, English Ivy, Kudzu, Bamboo and Autumn Olive. Phragmites common reed (Phragmites australis) Accidentally imported in ship ballast, European phragmites has spread up and down the East Coast for centuries, displacing millions of acres of wetland plants, including native phragmites. The Maryland Eastern Shore may harbor our only remaining native phragmites (Phragmites australis ssp. americanus.) Whereas native phragmites grows in sparse clumps and decomposes readily, European phragmites forms impenetrable monocultures more than 15-feet tall composed of both old and new canes. Subsequently, infested wetlands become dry land, wildlife habitat is destroyed, and a fire hazard created. Roots penetrate several feet deep and extend out 10 feet a season. Wind and water, carrying seed and rhizome/root fragments, have spread phragmites to tidal and nontidal wetland and dry lands, including ditches. It is extremely difficult to combat. English ivy (Hedera helix) Eurasian, not English, in origin, this evergreen vine threatens habitats at all heights. At ground level, its leaves shade out seedlings and herbs, forming acres of monoculture and attracting rodents. In trees, it engulfs branches, shading and slowly killing them. Its weight topples trees in wind, snow or icy conditions. It serves as a reservoir for bacterial leaf scorch, a serious disease of trees including maples, oaks and elms. Vines mature in trees, then flower and bear toxic berries which induce birds to vomit them out, ensuring spread. Any rooted piece can resprout. Kudzu (Pueraria montana var. lobata) “The vine that ate the South” was promoted as livestock forage, an ornamental, and for erosion control until the 1950s. -
Use of Duckweed, Lemna Minor, As a Protein Feedstuff in Practical Diets for Common Carp, Cyprinus Carpio, Fry
Turkish Journal of Fisheries and Aquatic Sciences 4: 105-109 (2004) Use of Duckweed, Lemna minor, as a Protein Feedstuff in Practical Diets for Common Carp, Cyprinus carpio, Fry Erdal Yılmaz1,*, øhsan Akyurt1, Gökhan Günal1 1 Mustafa Kemal University, Faculty of Fisheries and Aquaculture, 31034, Antakya, Hatay, Turkey. * Corresponding Author: Tel.: +90. 326 245 58 45/1315; Fax: +90. 326 245 58 17; Received 09 February 2005 E-mail: [email protected] Accepted 09 June 2005 Abstract The use of dried duckweed, Lemna minor, as a dietary protein source for Cyprinus carpio common carp fry reared in baskets was the topic of investigation in this study. Five diets with similar E:P ratios were fed to common carp fry with an average initial weight of 0.29 g for 90 days. A diet containing 5%, 10%, 15%, or 20% duckweed was substituted for the commercial 32% protein control-group diet, fed in normal rations to common carp. There was no significant difference between the growth performance of fish that were fed diets containing up to 20% duckweed and fish that were fed the control diet (P>0.05), except for the group of fish on the 15% duckweed diet. Also, no significant difference was observed among treatments with respect to feed utilization (P>0.05). While carcass lipid content increased, protein content of the fish fed a diet of 15% duckweed decreased compared to other groups (P<0.05). The results showed that a diet consisting of up to 20% content could be used as a complete replacement for commercial feed in diet formulation for common carp fry.