Freshwater Tidal Marsh State Rank: S1 - Critically Imperiled

Total Page:16

File Type:pdf, Size:1020Kb

Freshwater Tidal Marsh State Rank: S1 - Critically Imperiled Freshwater Tidal Marsh State Rank: S1 - Critically Imperiled Cross section showing characteristic species of bulrush, arrowhead, pickerel-weed, Freshwater Tidal Marsh. and water dock frequently occur. Freshwater cord-grass, threesquare, and water hemp are typical of rockier substrates. More sparsely vegetated mud flats include spike sedges, water purslane, water starwort and bittercress. Differentiating from Related Communities: The Illustrator: Brian Reid. key difference from other types of Freshwater Marsh is that Freshwater Tidal Marshes provide habitat for nesting Tidal Marshes are restricted to the area of Description: Freshwater Tidal on large rivers. Rocky shores have songbirds. Freshwater mussels are locally freshwater tidal action on coastal rivers Marshes occur on free-flowing coastal sparse, low growing annuals in patches of abundant. rivers just upstream of the salt front shallow soils. Mud flats in the river and streams above the zone of regular salt carried by incoming high tides. They are channel regularly have sediment water incursion. A difference from Examples with Public Access: flooded twice daily by the freshwater that deposition and prolonged inundation. Brackish Tidal Marshes is the lack salt West Newbury Conservation Area, West is backed up as it meets resistance from They are sparsely vegetated with a suite tolerant plants. Long’s bittercress, estuary Newbury; Willow Brook Farm Preserve the high tides downstream. Being along of low-growing plants. arrowhead, and estuary beggar-ticks, (Wildlands Trust), Pembroke; Stetson the shores of dynamic rivers, freshwater although shared with Brackish Tidal Meadows, Norwell; Mounces Meadow, tidal marshes are often structurally Characteristic Species: Freshwater Marshes, most commonly occur in the Marshfield. diverse. Freshwater tidal marsh represents Tidal Marshes are characterized by salt freshwater situation. Some other species the upstream end of a tidal gradient from intolerant plant species, typically a rich that co-occur in Freshwater and Brackish salt marsh, to brackish tidal marsh, to association of emergent grasses, sedges, Tidal Marshes are more likely to be found freshwater tidal marsh. Tidal amplitude rushes and forbs, with only occasional in the brackish condition: Lilaeopsis or may be up to 150 cm. Average annual shrubs in upper edges of the backmarsh. eastern grasswort, Atlantic mudwort, salinity is less than 0.5 ppt (from 0.5 ppt Narrow-leaved cattail and sweet flag water-pimpernel, Parker’s pipewort, and to 5 ppt salinity there is a gradient of occasionally forms exclusive stands, and Eaton’s beggar-ticks. Many of these are species to brackish conditions which have climbing hempweed often sprawls over uncommon, even in the appropriate an average annual salinity of 5-18 ppt). large patches of backmarsh. Dominant habitats. species include blue joint, lakeside and High marsh begins with an abrupt bank Habitat for Associated Fauna: of peat 1-3 feet above mean low water. It tussock sedges, narrow-leaved cattail, This community provides outstanding is often the most diverse vegetated zone wild rice, smartweeds, tearthumbs, general wildlife habitat, with abundant of the freshwater tidal marsh. Low marsh jewelweed, climbing hempweed, false food sources for migratory and wintering is on muddy or rocky sloping shores pimpernel, and sweet flag. Low marsh waterfowl, and is generally associated below the bank of high marsh particularly often has stand-forming emergent plants with tough mat-forming rhizomes that with river reaches with spawning habitat Freshwater Tidal Marshes are mixed resist erosion; annuals may also dominate for anadromous fisheries. It tends to have herbaceous marshes flooded by daily large sections of marsh. Large stands of more vertebrate species, such as tides, and occurring in the freshwater wild rice usually dominate muddy areas, freshwater snakes and muskrats, than do reach of coastal rivers; the Brackish Tidal Marshes. Freshwater Wild rice in a Freshwater Tidal Marsh. Photo: however stands of sweet flag, soft-stem Joanne Singfield, NHESP. From: Classification of Natural Communities of Massachusetts htthttpp://www;mass;gov/nhesp/://www;mass;gov/nhesp/ Updated: 2016 Natural Heritage & Endangered Species Program, Division of FishFisheeriesries & Wildlife, 1 Rabbit Hill Rd;, Westborough, M! 01581 (508) 389-6360 .
Recommended publications
  • Comparison of Swamp Forest and Phragmites Australis
    COMPARISON OF SWAMP FOREST AND PHRAGMITES AUSTRALIS COMMUNITIES AT MENTOR MARSH, MENTOR, OHIO A Thesis Presented in Partial Fulfillment of the Requirements for The Degree Master of Science in the Graduate School of the Ohio State University By Jenica Poznik, B. S. ***** The Ohio State University 2003 Master's Examination Committee: Approved by Dr. Craig Davis, Advisor Dr. Peter Curtis Dr. Jeffery Reutter School of Natural Resources ABSTRACT Two intermixed plant communities within a single wetland were studied. The plant community of Mentor Marsh changed over a period of years beginning in the late 1950’s from an ash-elm-maple swamp forest to a wetland dominated by Phragmites australis (Cav.) Trin. ex Steudel. Causes cited for the dieback of the forest include salt intrusion from a salt fill near the marsh, influence of nutrient runoff from the upland community, and initially higher water levels in the marsh. The area studied contains a mixture of swamp forest and P. australis-dominated communities. Canopy cover was examined as a factor limiting the dominance of P. australis within the marsh. It was found that canopy openness below 7% posed a limitation to the dominance of P. australis where a continuous tree canopy was present. P. australis was also shown to reduce diversity at sites were it dominated, and canopy openness did not fully explain this reduction in diversity. Canopy cover, disturbance history, and other environmental factors play a role in the community composition and diversity. Possible factors to consider in restoring the marsh are discussed. KEYWORDS: Phragmites australis, invasive species, canopy cover, Mentor Marsh ACKNOWLEDGEMENTS A project like this is only possible in a community, and more people have contributed to me than I can remember.
    [Show full text]
  • 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.
    [Show full text]
  • 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)
    [Show full text]
  • Coastal and Marine Ecological Classification Standard (2012)
    FGDC-STD-018-2012 Coastal and Marine Ecological Classification Standard Marine and Coastal Spatial Data Subcommittee Federal Geographic Data Committee June, 2012 Federal Geographic Data Committee FGDC-STD-018-2012 Coastal and Marine Ecological Classification Standard, June 2012 ______________________________________________________________________________________ CONTENTS PAGE 1. Introduction ..................................................................................................................... 1 1.1 Objectives ................................................................................................................ 1 1.2 Need ......................................................................................................................... 2 1.3 Scope ........................................................................................................................ 2 1.4 Application ............................................................................................................... 3 1.5 Relationship to Previous FGDC Standards .............................................................. 4 1.6 Development Procedures ......................................................................................... 5 1.7 Guiding Principles ................................................................................................... 7 1.7.1 Build a Scientifically Sound Ecological Classification .................................... 7 1.7.2 Meet the Needs of a Wide Range of Users ......................................................
    [Show full text]
  • 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.......................................................................................................
    [Show full text]
  • James T. Kirby, Jr
    James T. Kirby, Jr. Edward C. Davis Professor of Civil Engineering Center for Applied Coastal Research Department of Civil and Environmental Engineering University of Delaware Newark, Delaware 19716 USA Phone: 1-(302) 831-2438 Fax: 1-(302) 831-1228 [email protected] http://www.udel.edu/kirby/ Updated September 12, 2020 Education • University of Delaware, Newark, Delaware. Ph.D., Applied Sciences (Civil Engineering), 1983 • Brown University, Providence, Rhode Island. Sc.B.(magna cum laude), Environmental Engineering, 1975. Sc.M., Engineering Mechanics, 1976. Professional Experience • Edward C. Davis Professor of Civil Engineering, Department of Civil and Environmental Engineering, University of Delaware, 2003-present. • Visiting Professor, Grupo de Dinamica´ de Flujos Ambientales, CEAMA, Universidad de Granada, 2010, 2012. • Professor of Civil and Environmental Engineering, Department of Civil and Environmental Engineering, University of Delaware, 1994-2002. Secondary appointment in College of Earth, Ocean and the Environ- ment, University of Delaware, 1994-present. • Associate Professor of Civil Engineering, Department of Civil Engineering, University of Delaware, 1989- 1994. Secondary appointment in College of Marine Studies, University of Delaware, as Associate Professor, 1989-1994. • Associate Professor, Coastal and Oceanographic Engineering Department, University of Florida, 1988. • Assistant Professor, Coastal and Oceanographic Engineering Department, University of Florida, 1984- 1988. • Assistant Professor, Marine Sciences Research Center, State University of New York at Stony Brook, 1983- 1984. • Graduate Research Assistant, Department of Civil Engineering, University of Delaware, 1979-1983. • Principle Research Engineer, Alden Research Laboratory, Worcester Polytechnic Institute, 1979. • Research Engineer, Alden Research Laboratory, Worcester Polytechnic Institute, 1977-1979. 1 Technical Societies • American Society of Civil Engineers (ASCE) – Waterway, Port, Coastal and Ocean Engineering Division.
    [Show full text]
  • 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).
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • Freshwater Marsh and Coastal Salt Marsh. Both
    MARSH VEGETATION COMMUNITY There are two types of Marsh lands in San Diego County; Freshwater Marsh and Coastal Salt Marsh. Both of these communities are very important for wildlife, and both have had extensive reductions due to channelization, dredging and vegetation removal. Both communities have been reduced in area by 85-90 percent of their original area to less than 1,000 acres total. Coastal Salt Marsh is found within the tidal zone on the edge of lagoons and bays. The major locations of this community are the Tijuana Estuary, Penasquitos Lagoon and the mouth of the Santa Margarita River. Dominant plants in Coastal Salt Marsh are Glasswort (Salicornia), Alkali heath (Frankenia), Salt grass and Cordgrass. Two notable endangered birds occur within this community, the Light footed clapper rail and the Belding’s savannah sparrow. However, the Marsh lands are also important for shorebirds and the naturally occurring flow channels within Coastal Salt Marsh are important spawning areas for a number of fish species. Freshwater Marsh land is found along stream courses and near Riparian wetland areas. It was originally found near natural springs and ponded areas within the major stream channels. It has been affected by channelization and clearing of vegetation within stream channels. Dominant plants within Freshwater Marsh include rushes, cattails, bulrushes (or tules) and several species of small willows. There is often open water in depressions or natural springs. Freshwater Marsh is home to a number of species of birds including the Yellowthroat, a species of Warbler, several species of small herons as well as rails. Freshwater Marsh in its natural state has also served as habitat for native frog species, several of which are now endangered.
    [Show full text]
  • Ecosystem Element Conceptual Model Tidal Marsh
    Sacramento-San Joaquin Delta Regional Ecosystem Restoration Implementation Plan Ecosystem Element Conceptual Model Tidal Marsh Prepared by: Ronald T. Kneib, University of Georgia Marine Institute [email protected] and • Charles A. Simenstad, School of Aquatic & Fisheries Sciences, University of Washington • Matt L. Nobriga, CALFED Science Program • Drew M. Talley, San Francisco Bay National Estuarine Research Reserve, San Francisco State University, Romberg Tiburon Center Date of Model: October 2008 Status of Peer Review: Completed peer review on October 2008. Model content and format are suitable and model is ready for use in identifying and evaluating restoration actions. Suggested Citation: Kneib R, Simenstad C, Nobriga M, Talley D. 2008. Tidal marsh conceptual model. Sacramento (CA): Delta Regional Ecosystem Restoration Implementation Plan. For further inquiries on the DRERIP conceptual models, please contact Brad Burkholder at [email protected] or Steve Detwiler at [email protected]. PREFACE This Conceptual Model is part of a suite of conceptual models which collectively articulate the current scientific understanding of important aspects of the Sacramento-San Joaquin River Delta ecosystem. The conceptual models are designed to aid in the identification and evaluation of ecosystem restoration actions in the Delta. These models are designed to structure scientific information such that it can be used to inform sound public policy. The Delta Conceptual Models include both ecosystem element models (including process, habitat, and stressor models) and species life history models. The models were prepared by teams of experts using common guidance documents developed to promote consistency in the format and terminology of the models http://www.delta.dfg.ca.gov/erpdeltaplan/science_process.asp .
    [Show full text]
  • Responses of Tidal Freshwater and Brackish Marsh Macrophytes to Pulses of Saline Water Simulating Sea Level Rise and Reduced Discharge
    Wetlands (2018) 38:885–891 https://doi.org/10.1007/s13157-018-1037-2 ORIGINAL RESEARCH Responses of Tidal Freshwater and Brackish Marsh Macrophytes to Pulses of Saline Water Simulating Sea Level Rise and Reduced Discharge Fan Li1 & Steven C. Pennings1 Received: 7 June 2017 /Accepted: 16 April 2018 /Published online: 25 April 2018 # Society of Wetland Scientists 2018 Abstract Coastal low-salinity marshes are increasingly experiencing periodic to extended periods of elevated salinities due to the com- bined effects of sea level rise and altered hydrological and climatic conditions. However, we lack the ability to predict detailed vegetation responses, especially for saline pulses that are more realistic in nature than permanent saline presses. In this study, we exposed common freshwater and brackish plants to different durations (1–31 days per month for 3 months) of saline water (salinity of 5). We found that Zizaniopsis miliacea was more tolerant to salinity than the other two freshwater species, Polygonum hydropiperoides and Pontederia cordata. We also found that Zizaniopsis miliacea belowground and total biomass appeared to increase with salinity pulses up to 16 days in length, although this relationship was quite variable. Brackish plants, Spartina cynosuroides, Schoenoplectus americanus and Juncus roemerianus, were unaffected by the experimental treatments. Our ex- periment did not evaluate how competitive interactions would further affect responses to salinity but our results suggest the hypothesis that short pulses of saline water will increase the cover of Zizaniopsis miliacea and decrease the cover of Polygonum hydropiperoides and Pontederia cordata in tidal freshwater marshes, thereby reducing diversity without necessarily affecting total plant biomass.
    [Show full text]