Ecosystem Element Conceptual Model Tidal Marsh
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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) -
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 ...................................................... -
A Brief Introduction to the Shantou Intertidal Wetland, Southern China
AA BriefBrief IntroductionIntroduction toto thethe ShantouShantou IntertidalIntertidal Wetland,Wetland, SouthernSouthern ChinaChina Y.Y. W.W. ZhouaZhoua*.*. G.G. Z.Z. ChenChen SchoolSchool ofof EnvironmentalEnvironmental ScienceScience andand Engineering,Engineering, SunSun YatYat--sensen University,University, Guangzhou,Guangzhou, ChinaChina PR;PR; ** EE--mail:mail: [email protected]@163.com 11 IntroductionIntroduction • Shantou City is one of the most developed cities in southeast coastal area of China. • It had a high population of 4,846,400 . The population density was 2,348 per km2, GDP was 1,700 US $,in 2003. • The current use of the Shantou Intertidal Wetland includes: • briny and limnetic aquaculture, • reclamation for farmland and municipal estate, • transition to the salt field or tourism park, • natural wetland as the habitat of resident and migratory wildlife. 2.2. CharacteristicsCharacteristics ofof ShantouShantou IntertidalIntertidal WetlandWetland 2.1 Environmental characteristics The total area of the Shantou Intertidal Wetland is 1,435.29 ha . The demonstration site’s area is 3,475.2 ha , including 4 parts: Fig. 1 Demonstrated content of sub demonstration sites No Demon site Demonstrated Content Area/ha 1 Hexi biodiversity of water weed 512.4 2 Sanyuwei aquiculture and the biological treatment of waste water 1639.5 3 Suaiwang secondary mangrove for birds habitat 388.7 4 Waisha Eco-tourism 934.6 2.22.2 ClimateClimate • The climate is warm all year round with high temperatures and abundant light, and clearly differentiated dry and wet seasons. • Mean annual duration of sunshine: 954.2 hrs. • Historical average air temperature : 23.1 °C. • Average high temperature :38.8 °C • Average low temperature : 15.8 °C. -
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. -
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. -
Coastal Wetland Trends in the Narragansett Bay Estuary During the 20Th Century
u.s. Fish and Wildlife Service Co l\Ietland Trends In the Narragansett Bay Estuary During the 20th Century Coastal Wetland Trends in the Narragansett Bay Estuary During the 20th Century November 2004 A National Wetlands Inventory Cooperative Interagency Report Coastal Wetland Trends in the Narragansett Bay Estuary During the 20th Century Ralph W. Tiner1, Irene J. Huber2, Todd Nuerminger2, and Aimée L. Mandeville3 1U.S. Fish & Wildlife Service National Wetlands Inventory Program Northeast Region 300 Westgate Center Drive Hadley, MA 01035 2Natural Resources Assessment Group Department of Plant and Soil Sciences University of Massachusetts Stockbridge Hall Amherst, MA 01003 3Department of Natural Resources Science Environmental Data Center University of Rhode Island 1 Greenhouse Road, Room 105 Kingston, RI 02881 November 2004 National Wetlands Inventory Cooperative Interagency Report between U.S. Fish & Wildlife Service, University of Massachusetts-Amherst, University of Rhode Island, and Rhode Island Department of Environmental Management This report should be cited as: Tiner, R.W., I.J. Huber, T. Nuerminger, and A.L. Mandeville. 2004. Coastal Wetland Trends in the Narragansett Bay Estuary During the 20th Century. U.S. Fish and Wildlife Service, Northeast Region, Hadley, MA. In cooperation with the University of Massachusetts-Amherst and the University of Rhode Island. National Wetlands Inventory Cooperative Interagency Report. 37 pp. plus appendices. Table of Contents Page Introduction 1 Study Area 1 Methods 5 Data Compilation 5 Geospatial Database Construction and GIS Analysis 8 Results 9 Baywide 1996 Status 9 Coastal Wetlands and Waters 9 500-foot Buffer Zone 9 Baywide Trends 1951/2 to 1996 15 Coastal Wetland Trends 15 500-foot Buffer Zone Around Coastal Wetlands 15 Trends for Pilot Study Areas 25 Conclusions 35 Acknowledgments 36 References 37 Appendices A. -
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. -
Upside-Down'' Estuaries of the Florida Everglades
Limnol. Oceanogr., 51(1, part 2), 2006, 602±616 q 2006, by the American Society of Limnology and Oceanography, Inc. Relating precipitation and water management to nutrient concentrations in the oligotrophic ``upside-down'' estuaries of the Florida Everglades Daniel L. Childers1 Department of Biological Sciences and SERC, Florida International University, Miami, Florida 33199 Joseph N. Boyer Southeast Environmental Research Center, Florida International University, Miami, Florida 33199 Stephen E. Davis Department of Wildlife and Fisheries Sciences, Texas A&M University, College Station, Texas 77843 Christopher J. Madden and David T. Rudnick Coastal Ecosystems Division, South Florida Water Management District, 3301 Gun Club Road, West Palm Beach, Florida 33416 Fred H. Sklar Everglades Division, South Florida Water Management District, 3301 Gun Club Road, West Palm Beach, Florida 33416 Abstract We present 8 yr of long-term water quality, climatological, and water management data for 17 locations in Everglades National Park, Florida. Total phosphorus (P) concentration data from freshwater sites (typically ,0.25 mmol L21,or8mgL21) indicate the oligotrophic, P-limited nature of this large freshwater±estuarine landscape. Total P concentrations at estuarine sites near the Gulf of Mexico (average ø0.5 m mol L21) demonstrate the marine source for this limiting nutrient. This ``upside down'' phenomenon, with the limiting nutrient supplied by the ocean and not the land, is a de®ning characteristic of the Everglade landscape. We present a conceptual model of how the seasonality of precipitation and the management of canal water inputs control the marine P supply, and we hypothesize that seasonal variability in water residence time controls water quality through internal biogeochemical processing. -
Mangroves and Saltmarshes of Moreton Bay
https://moretonbayfoundation.org/ 1 Moreton Bay Quandamooka & Catchment: Past, present, and future Chapter 5 Habitats, Biodiversity and Ecosystem Function Mangroves and saltmarshes of Moreton Bay Abstract The mangroves and saltmarshes of Moreton Bay comprising 18,400 ha are important habitats for biodiversity and providing ecosystem services. Government policy and legislation largely reflects their importance with protection provided through a range of federal and state laws, including the listing of saltmarsh communities in 2013 under the Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act). Local communities also conserve and manage mangroves and saltmarshes. Recent scientific research on these ecosystems in Moreton Bay has described food webs, habitat use by fauna, carbon sequestration and effects of climate change. The area of saltmarsh has declined by 64% since 1955 due to mangrove encroachment into saltmarsh habitats and past conversion to rural and urban land uses. Mangrove encroachment into saltmarsh habitats, which has been reported in other locations in Australia and across the world, has increased the area of mangrove habitat by 6.4% over the same period. This is consistent with predictions of habitat changes under climate change, and demonstrates the need for management strategies that ensure these ecosystems are maintained. Keywords: coastal wetlands, intertidal, wetland management, EPBC Act, wetland change, drivers of wetland change, South East Queensland, soil carbon stocks Introduction Mangroves and saltmarshes, which are components of the estuarine wetlands of Moreton Bay, are dominated by salt-tolerant vegetation that occurs from approximately mean sea level to the highest astronomical tidal plane. They occur within the river systems and tidal creeks of Moreton Bay as well as on the comparatively open coasts of the Bay where they fringe both islands and the mainland. -
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. -
Full Document (Pdf 2154
White Paper Research Project T1803, Task 35 Overwater Whitepaper OVERWATER STRUCTURES: MARINE ISSUES by Barbara Nightingale Charles A. Simenstad Research Assistant Senior Fisheries Biologist School of Marine Affairs School of Aquatic and Fishery Sciences University of Washington Seattle, Washington 98195 Washington State Transportation Center (TRAC) University of Washington, Box 354802 University District Building 1107 NE 45th Street, Suite 535 Seattle, Washington 98105-4631 Washington State Department of Transportation Technical Monitor Patricia Lynch Regulatory and Compliance Program Manager, Environmental Affairs Prepared for Washington State Transportation Commission Department of Transportation and in cooperation with U.S. Department of Transportation Federal Highway Administration May 2001 WHITE PAPER Overwater Structures: Marine Issues Submitted to Washington Department of Fish and Wildlife Washington Department of Ecology Washington Department of Transportation Prepared by Barbara Nightingale and Charles Simenstad University of Washington Wetland Ecosystem Team School of Aquatic and Fishery Sciences May 9, 2001 Note: Some pages in this document have been purposefully skipped or blank pages inserted so that this document will copy correctly when duplexed. TECHNICAL REPORT STANDARD TITLE PAGE 1. REPORT NO. 2. GOVERNMENT ACCESSION NO. 3. RECIPIENT'S CATALOG NO. WA-RD 508.1 4. TITLE AND SUBTITLE 5. REPORT DATE Overwater Structures: Marine Issues May 2001 6. PERFORMING ORGANIZATION CODE 7. AUTHOR(S) 8. PERFORMING ORGANIZATION REPORT NO. Barbara Nightingale, Charles Simenstad 9. PERFORMING ORGANIZATION NAME AND ADDRESS 10. WORK UNIT NO. Washington State Transportation Center (TRAC) University of Washington, Box 354802 11. CONTRACT OR GRANT NO. University District Building; 1107 NE 45th Street, Suite 535 Agreement T1803, Task 35 Seattle, Washington 98105-4631 12. -
Mangrove Elevation-Sea Level Rise Response Model
Mangrove sea-level rise response modeling to inform planning Karen Thorne & Kevin Buffington USGS Western Ecological Research Center RAE Conference December 12th, 10:30-12 “A Web-Based Interactive Decision-Support Tool for Adaptation of Coastal Urban and Natural Ecosystems (ACUNE) in Southwest Florida” Project and Science Lead: Peter Sheng, University of Florida ([email protected]) Coordination Lead: Michael Savarese, Florida Gulf Coast University ([email protected]) Team: Christine Angelini, Mike Barry, Kevin Buffington, Justin Davis, Felix Jose, Ken Krause, David Letson, Vladimir Paramygin, Karen Thorne, Chuen “Andy” Hsu, Adail Rivera-Nieves, Sean Sharp, Kun Yang We are developing ACUNE to enable Adaption of Coastal Urban and Natural Systems for A Sustainable & Economically Healthy SW Florida in the Context of Increasing Future Inundation Risk Study Domain Largest Mangrove Forest in Gulf of Mexico region Ecosystem Services: Ecosystem Diversity, Fishery Habitat, Flood Protection Coastal Wetland Vulnerability to Sea-level rise • Projected sea-level rise pose a risk to coastal wetlands, including tidal marshes and mangroves • Mangroves provide wildlife habitat and valuable ecosystem services, including protecting infrastructure from flooding and storms • Mangroves provide a lot of carbon storage • Coastal wetlands require mineral and organic sediment inputs to build elevations to keep pace with sea-level rise. Red, white, and black mangroves in FL Mangrove ecosystems From: Lee et al. Global Ecology and Biogeography, 2014, 23: 726–743