Habitat Comparison Walk Grades
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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) -
The Evolution of the Artificial Wildbird Tidal Mudflat in Fukuoka, Japan
1 The Evolution of the MIA DOCTO + SCOTT WALLS Jacob Bintliff, Mariana Chavez, Daniela Peña Corvillon, Artificial Wildbird Tidal Johanna Hoffman, Katelyn Walker, UC Berkeley, LA 205 Studio Mudflat in Fukuoka, Japan Spring 2012 2 PRESENTATION CONTENT INTRODUCTION // SCIENTIFIC ANALYSIS // WETLAND DESIGN // HUMAN INTERFACE // CONCLUSIONS 3 CONTEXT 4 5 6 CONTEXT BEFORE PRESENT 7 ISLAND CITY 8 9 ITERATIONS ORIGINAL WETLAND PLAN 10 ITERATIONS JAPAN STUDENT WORKSHOP 11 ITERATIONS 2008 Land Use Plan ~8.5 - 9 ha ~12 ha ~10 ha ~10 ~7 ha Setup of the central area ~8.75 ha ~38.25 ha We will establish a lively ~7 ha interactive space by inviting urban functions such as commercial and ~ 6.75 ha corporate functions, and dissemination of information on education, ~2.25 ha Wild Bird Park 3.9 ha 3.1 ha School and Amenities culture, and art. Further, public transportation Green Space facilities and facilities for 4.1 ha convenience are invited Assigned Facilities Teriha Town to improve the business Hospital ~18 ha environment in the area. Apartments 4.1+ ha Joint Independent Houses Spcialist Clinic 1.8 ha ~1.5 ha Commercial Elderly Elderly Center? Center Planned Subdivision 1.6 ha 1.2 ha Coporate (Sold) 0.9 ha Planned Use/Mixed Use Idustrial and hatches based on legend color code and denote use type Research & Development Currently Built Port Warf 1000 m UC BERKELEY LAND USE PLAN 12 ITERATIONS UC BERKELEY LAND USE PLAN 13 ITERATIONS 16 Hectare Wild Bird Park UC BERKELEY - JAPAN WETLAND DESIGN 14 DESIGN GOALS Provide natural habitat for migrating bird species -
A Survey of the Nation's Lakes
A Survey of the Nation’s Lakes – EPA’s National Lake Assessment and Survey of Vermont Lakes Vermont Agency of Natural Resources Department of Environmental Conservation - Water Quality Division 103 South Main 10N Waterbury VT 05671-0408 www.vtwaterquality.org Prepared by Julia Larouche, Environmental Technician II January 2009 Table of Contents List of Tables and Figures........................................................................................................................................................................... ii Introduction................................................................................................................................................................................................. 1 What We Measured..................................................................................................................................................................................... 4 Water Quality and Trophic Status Indicators.......................................................................................................................................... 4 Acidification Indicator............................................................................................................................................................................ 4 Ecological Integrity Indicators................................................................................................................................................................ 4 Nearshore Habitat Indicators -
Moe Pond Limnology and Fisii Population Biology: an Ecosystem Approach
MOE POND LIMNOLOGY AND FISII POPULATION BIOLOGY: AN ECOSYSTEM APPROACH C. Mead McCoy, C. P.Madenjian, J. V. Adall1s, W. N. I-Iannan, D. M. Warner, M. F. Albright, and L. P. Sohacki BIOLOGICAL FIELD STArrION COOPERSTOWN, NEW YORK Occasional Paper No. 33 January 2000 STATE UNIVERSITY COLLEGE AT ONEONTA ACKNOWLEDGMENTS I wish to express my gratitude to the members of my graduate committee: Willard Harman, Leonard Sohacki and Bruce Dayton for their comments in the preparation of this manuscript; and for the patience and understanding they exhibited w~lile I was their student. ·1 want to also thank Matthew Albright for his skills in quantitative analyses of total phosphorous and nitrite/nitrate-N conducted on water samples collected from Moe Pond during this study. I thank David Ramsey for his friendship and assistance in discussing chlorophyll a methodology. To all the SUNY Oneonta BFS interns who lent-a-hand during the Moe Pond field work of 1994 and 1995, I thank you for your efforts and trust that the spine wounds suffered were not in vain. To all those at USGS Great Lakes Science Center who supported my efforts through encouragement and facilities - Jerrine Nichols, Douglas Wilcox, Bruce Manny, James Hickey and Nancy Milton, I thank all of you. Also to Donald Schloesser, with whom I share an office, I would like to thank you for your many helpful suggestions concerning the estimation of primary production in aquatic systems. In particular, I wish to express my appreciation to Charles Madenjian and Jean Adams for their combined quantitative prowess, insight and direction in data analyses and their friendship. -
Journal of the Oklahoma Native Plant Society, Volume 2, Number 1
54 Oklahoma Native Plant Record Volume 2, Number 1, December 2002 Schoenoplectus hallii and S. saximontanus 2000 Wichita Mountain Wildlife Refuge Survey Dr. Lawrence K. Magrath Curator-USAO (OCLA) Herbarium Chickasha, OK 73018-5358 A survey to determine locations of populations of Schoenoplectus hallii and S. saximontanus was conducted at Wichita Mountains Wildlife Refuge in August and September 2000. One or both species were found at 20 of the 134 locations surveyed. A distinctive terminal achene character was found specifically that the transverse ridges of S. hallii appeared to be rounded and S. saximontanus appeared to be rounded with a projecting narrow wing. Basal macroachenes have not yet been properly described but are borne singly at the base of each culm and are about 3-4 times larger than the terminal achenes. It is speculated that amphicarpy may be related to grazing pressure, the basal macroachene being produced even if the upper portion is consumed, as a response to grazing. Both species are grazed/disturbed by bison, elk, and longhorns on the Refuge. Introduction the drawdown mud, sand, or gravel flats. A survey to determine locations of However in some places they occur in shallow populations of Schoenoplectus hallii (A. Gray) water up to a depth of about a foot [30.5cm]. S.G. Smith (Hall’s bulrush) and S. saximontanus They seem to compete with perennial emergent (Fernald) J. Raynal (Rocky Mountain bulrush) plants and with most emergent annuals. was conducted on the Wichita Mountains In addition to the 36 sites that I Wildlife Refuge during late August through personally examined, WMWR staff examined September 2000. -
RIPARIAN AREASAREAS Updatedupdated June 21, 2012
RIPARIAN AREASAREAS UpdatedUpdated June 21, 2012 A 2012 Critical Areas Update Fact Sheet THE ROLE OF RIPARIAN AREAS Some of our most valuable habitat for the diverse Trees that fall into the wildlife in Thurston County – “riparian habitat” – is water form sheltered pools found along water bodies such as rivers, streams, where fi sh can lay eggs. lakes and marine (salt water) shorelines. In the past, The trees and pools also these areas have been referred to as buffers, and the supply insects and organic terms are still used interchangeably in some cases. materials for the aquatic food chain. Approximately Riparian habitat refers to the transitional areas 90 percent of all wildlife use between the upland environment and the water. riparian areas for part or all Riparian habitats moderate the temperature of water of their life cycles. bodies, help prevent erosion, and provide a home for many types of animals and vegetation. Although Potential amendments to the Critical Areas Ordinance riparian areas are located alongside the water, they seek to protect habitat and healthy functioning also provide habitat within the water. ecosystems in order to support viable populations of fi sh and wildlife in Thurston County. ABOUT WATER TYPE CLASSIFICATIONS Like the existing Critical Areas Ordinance, the The DNR classifi cations are: potential amendments would set riparian areas according to how the streams and water bodies • Type S: Streams and water bodies that are are classifi ed or “typed” by the state Department designated “Shorelines of the State” as defi ned in of Natural Resources. The water types are based chapter 90.58.030 RCW. -
Wetlands, Biodiversity and the Ramsar Convention
Wetlands, Biodiversity and the Ramsar Convention Wetlands, Biodiversity and the Ramsar Convention: the role of the Convention on Wetlands in the Conservation and Wise Use of Biodiversity edited by A. J. Hails Ramsar Convention Bureau Ministry of Environment and Forest, India 1996 [1997] Published by the Ramsar Convention Bureau, Gland, Switzerland, with the support of: • the General Directorate of Natural Resources and Environment, Ministry of the Walloon Region, Belgium • the Royal Danish Ministry of Foreign Affairs, Denmark • the National Forest and Nature Agency, Ministry of the Environment and Energy, Denmark • the Ministry of Environment and Forests, India • the Swedish Environmental Protection Agency, Sweden Copyright © Ramsar Convention Bureau, 1997. Reproduction of this publication for educational and other non-commercial purposes is authorised without prior perinission from the copyright holder, providing that full acknowledgement is given. Reproduction for resale or other commercial purposes is prohibited without the prior written permission of the copyright holder. The views of the authors expressed in this work do not necessarily reflect those of the Ramsar Convention Bureau or of the Ministry of the Environment of India. Note: the designation of geographical entities in this book, and the presentation of material, do not imply the expression of any opinion whatsoever on the part of the Ranasar Convention Bureau concerning the legal status of any country, territory, or area, or of its authorities, or concerning the delimitation of its frontiers or boundaries. Citation: Halls, A.J. (ed.), 1997. Wetlands, Biodiversity and the Ramsar Convention: The Role of the Convention on Wetlands in the Conservation and Wise Use of Biodiversity. -
Analyzing Trends of Dike-Ponds Between 1978 and 2016 Using Multi-Source Remote Sensing Images in Shunde District of South China
sustainability Article Analyzing Trends of Dike-Ponds between 1978 and 2016 Using Multi-Source Remote Sensing Images in Shunde District of South China Fengshou Li 1, Kai Liu 1,* , Huanli Tang 2, Lin Liu 3,4,* and Hongxing Liu 4,5 1 Guangdong Key Laboratory for Urbanization and Geo-simulation, Guangdong Provincial Engineering Research Center for Public Security and Disaster, School of Geography and Planning, Sun Yat-Sen University, Guangzhou 510275, China; [email protected] 2 Guangzhou Zengcheng District Urban and Rural Planning and Surveying and Mapping Geographic Information Institute, Guangzhou 511300, China; [email protected] 3 Center of Geo-Informatics for Public Security, School of Geographic Sciences, Guangzhou University, Guangzhou 510006, China 4 Department of Geography and Geographic Information Science, University of Cincinnati, Cincinnati, OH 45221, USA; [email protected] 5 Department of Geography, the University of Alabama, Tuscaloosa, AL 35487, USA * Correspondence: [email protected] (K.L.); [email protected] (L.L.); Tel.: +86-020-8411-3044 (K.L.); +1-513-556-3429 (L.L.); Fax: +86-020-8411-3057 (K.L. & L.L.) Received: 27 August 2018; Accepted: 26 September 2018; Published: 30 September 2018 Abstract: Dike-ponds have experienced significant changes in the Pearl River Delta region over the past several decades, especially since China’s economic reform, which has seriously affected the construction of ecological environments. In order to monitor the evolution of dike-ponds, in this study we use multi-source remote sensing images from 1978 to 2016 to extract dike-ponds in several periods using the nearest neighbor classification method. -
MUD CREATURE STUDY Overview: the Mudflats Support a Tremendous Amount of Life
MUD CREATURE STUDY Overview: The mudflats support a tremendous amount of life. In this activity, students will search for and study the creatures that live in bay mud. Content Standards Correlations: Science p. 307 Grades: K-6 TIME FRAME fOR TEACHING THIS ACTIVITY Key Concepts: Mud creatures live in high abundance in the Recommended Time: 30 minutes mudflats, providing food for Mud Creature Banner (7 minutes) migratory ducks and shorebirds • use the Mud Creature Banner to introduce students to mudflat and the endangered California habitat clapper rail. When the tide is out, Mudflat Food Pyramid (3 minutes) the mudflats are revealed and birds land on the mudflats to feed. • discuss the mudflat food pyramid, using poster Mud Creature Study (20 minutes) Objectives: • sieve mud in sieve set, using slough water Students will be able to: • distribute small samples of mud to petri dishes • name and describe two to three • look for mud creatures using hand lenses mud creatures • describe the mudflat food • use the microscopes for a closer view of mud creatures pyramid • if data sheets and pencils are provided, students can draw what • explain the importance of the they find mudflat habitat for migratory birds and endangered species Materials: How THIS ACTIVITY RELATES TO THE REFUGE'S RESOURCES Provided by the Refuge: What are the Refuge's resources? • 1 set mud creature ID cards • significant wildlife habitat • 1 mud creature flannel banner • endangered species • 1 mudflat food pyramid poster • 1 mud creature ID book • rhigratory birds • 1 four-layered sieve set What makes it necessary to manage the resources? • 1 dish of mud and trowel • Pollution, such as oil, paint, and household cleaners, when • 1 bucket of slough water dumped down storm drains enters the slough and mudflats and • 1 pitcher of slough water travels through the food chain, harming animals. -
Erosion and Accretion on a Mudflat: the Importance of Very 10.1002/2016JC012316 Shallow-Water Effects
PUBLICATIONS Journal of Geophysical Research: Oceans RESEARCH ARTICLE Erosion and Accretion on a Mudflat: The Importance of Very 10.1002/2016JC012316 Shallow-Water Effects Key Points: Benwei Shi1,2 , James R. Cooper3 , Paula D. Pratolongo4 , Shu Gao5 , T. J. Bouma6 , Very shallow water accounted for Gaocong Li1 , Chunyan Li2 , S.L. Yang5 , and YaPing Wang1,5 only 11% of the duration of the entire tidal cycle, but accounted for 1Ministry of Education Key Laboratory for Coast and Island Development, Nanjing University, Nanjing, China, 2Department 35% of bed-level changes 3 Erosion and accretion during very of Oceanography and Coastal Sciences, Louisiana State University, Baton Rouge, LA, USA, Department of Geography and 4 shallow water stages cannot be Planning, School of Environmental Sciences, University of Liverpool, Liverpool, UK, CONICET – Instituto Argentino de neglected when modeling Oceanografıa, CC 804, Bahıa Blanca, Argentina, 5State Key Laboratory of Estuarine and Coastal Research, East China morphodynamic processes Normal University, Shanghai, China, 6NIOZ Royal Netherlands Institute for Sea Research, Department of Estuarine and This study can improve our understanding of morphological Delta Systems, and Utrecht University, Yerseke, The Netherlands changes of intertidal mudflats within an entire tidal cycle Abstract Understanding erosion and accretion dynamics during an entire tidal cycle is important for Correspondence to: assessing their impacts on the habitats of biological communities and the long-term morphological Y. P. Wang, evolution of intertidal mudflats. However, previous studies often omitted erosion and accretion during very [email protected] shallow-water stages (VSWS, water depths < 0.20 m). It is during these VSWS that bottom friction becomes relatively strong and thus erosion and accretion dynamics are likely to differ from those during deeper Citation: flows. -
Bolinas Lagoon Ecosystem Restoration Feasibility Project
Bolinas Lagoon Ecosystem Restoration Feasibility Project Marin County Open Space District With Funding from the California State Coastal Conservancy & the U.S. Army Corps of Engineers July 2006 Bolinas Lagoon Ecosystem Restoration Feasibility Project Final Public Reports Table of Contents Volume I I Executive Summary II Projecting the Future of Bolinas Lagoon ¢¡¤£ ¥ £ ¦¨§©£ ¥ ¥ £ ¤£ ¢ Volume II III Recent (1850-2005) and late Holocene (400-1850) Sedimentation Rates at Bolinas Lagoon ¤!#"%$&" '(!)*+#, - ./1032#4 5(276 2#8 IV Conceptual Littoral Sediment Budget 9¢:¤; < ; =¨>©; < < ; ? @ABCAA D¤E; ? F GA V Project Reformulation Advisory Committee Summary of Draft Public Report S S TT H¢I¢J%KMLN7OPORQ VI Peer Review and Public Comments on Previous Drafts Reports with Responses U¢V¤W X W Y¨Z©W X X W [ \]^_]] `¤aW [ b c] de¢f a. Peer Reviews of Administrative Draft Report and Responses b. Public Comment Letters on Public Draft Report c. Response to Public Comment Letters Report Availability The report is available in multiple formats: • The report may be read and downloaded from www.marinopenspace.org • CDs are available on request by writing to William Carmen, Project Manager Bolinas Lagoon Ecosystem Restoration Feasibility Study MCOSD 3501 Civic Center Drive Suite 415 San Rafael, CA 94903 Or email: [email protected] • Hard copies of the report are on loan at the following locations: Marin County Library Branches: Bolinas, Stinson Beach, Civic Center, Fairfax, Inverness, Marin City, Novato, Pt. Reyes Station & San Geronimo Valley. -
Homeowners Guide to Protecting Ponds and Wetlands
Homeowners Guide to Protecting Ponds and Wetlands Weston has several small ponds throughout town. Most of these ponds were originally man-made either by building a dam (i.e. Hobbs Pond and College Pond) or by dredging an area along a stream. Weston’s ponds provide habitat for numerous birds, fish, turtles, frogs, and mammals. Because these ponds are often shallow, controlling aquatic plants from over-taking them can be a challenge. Several Weston homeowners have hired professionals to prepare and implement pond management programs. These programs often involve hand removal and/or chemical treatment to control nuisance or invasive aquatic plants. However, it’s important for pond abutters to know that they too directly affect pond health and water quality. This brochure lists several ways homeowners can help protect Weston’s ponds and wetlands. 1. Nature likes it Messy Some people want to “clean up” nature to create a park like appearance. However, wildlife often needs thick tangles of undergrowth, leaf litter, and deadwood to survive. Aquatic plants are a vital part of any healthy pond and wetland ecosystem. Plants and algae provide many benefits to the pond: roots help to prevent muddy water by stabilizing the pond bottom and banks. Pond plants use nutrients that may be taken up by nuisance algae. The stems, roots, and leaves of pond plants serve as important wildlife habitat for small pond animals such as dragonfly nymphs, tadpoles, and crayfish. If you are concerned that there are too many nuisance plants or algae growing in your pond, the law requires that you speak to the Conservation Commission prior to doing any vegetation removal or chemical treatments within or near the pond.