Reviving Dead Zones
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Salt Point State Marine Conservation Area North Central California Marine Protected Areas (Mpas), Established May 2010
Salt Point State Marine Conservation Area North Central California Marine Protected Areas (MPAs), Established May 2010 Red abalone Blue rockfish Salt Point SMCA (Haliotis rufescens) (Sebastes mystinus) Photo by Brian Owens Photo by CDFW Photo by Kevin Joe Site Overview Photos are representative of the North Central Coast Region and may not be within this MPA. What is an MPA? MPAs are a type of marine managed area (MMA) where marine or estuarine waters are set aside primarily to protect or conserve marine life and associated habitats. California has a coastal network of 124 protected areas designed to help increase the coherence and effectiveness of protecting the state’s marine life, habitats, and ecosystems. The network includes three types of MPA: state marine reserve (SMR), state marine conservation area (SMCA), and state marine park (SMP); one MMA: state marine recreational management area (SMRMA); and special closures. There are 119 MPAs, 5 MMAs and 15 special closures, each with unique boundaries and regulations in the network. Non-consumptive activities, restoration, and permitted scientific research are allowed. What is an SMCA? An SMCA is a type of MPA that protects resources by allowing for only specific types of recreational and/or commercial take to occur. (Area restrictions are defined in Title 14, Section 632(a)(1)(C)). Salt Point SMCA Overview Salt Point SMCA Key Habitats MPA size: 1.84 square miles Beaches: 0.62 miles Depth range: 0 to 226 feet Rocky shores: 4.30 miles Along-shore span (shoreline): 2.40 miles Sand (all depths): 1.14 square miles Rock (all depths): 0.40 square miles Where is Salt Point SMCA? Average Kelp (1989 to 2008): 0.11 square miles Unidentified (all depths): 0.28 square miles Boundaries and Regulations Boundary: This area is bounded by the mean high tide line and straight lines connecting the following points in the order listed: 38° 35.600' N. -
Hypoxia Infographic
Understanding HYP XIA Hypoxia is an environmental phenomenon where the concentration of dissolved oxygen in the water column decreases to a level that can no longer 1 support living aquatic organisms. The level is often considered to be 2 mg O2 per liter of water or lower. Hypoxic and anoxic (no oxygen) waters have existed throughout geologic time, but their occurrence in shallow coastal and estuarine areas appears to be increasing as a result of human activities. 2 What causes hypoxia? In 2015, scientists determined the Gulf of Mexico dead zone to be 6,474 square miles, which is an area about the size of Connecticut and Rhode Island combined. 3 Major events leading to the formation of hypoxia in the Gulf of Mexico include: Coastal Hypoxia and Eutrophication Sunlight Watershed Areas of anthropogenically-influenced n> In the past century, Hypoxia has become a global concern with estuarine and coastal hypoxia. 550 over 550 coastal areas identified as experiencing this issue. 4 Runoff and nutrient 1 loading of the Mississippi River. Nutrient-rich water from the Mississippi River forms 1960 a surface lens. 1970 Combined, Dead Zones 1980 cover 4x the area of the 1990 Great Lakes. % 2000 Nutrient-enhanced 4 2 primary production, Only a small fraction of the 550-plus Number of dead zones has approximately Today, there is currently about 1,148,000 km2 or eutrophication. hypoxia zones exhibited any signs doubled each decade since the 1960’s. 5 of seabed covered by Oxygen Minimum Phytoplankton growth of improvement. 5 Zones (OMZs) (<0.5 ml of O /liter) 5 is fueled by nutrients. -
Gulf of Mexico Hypoxia Monitoring Strategy
Gulf of Mexico Hypoxia Monitoring Strategy Hypoxia Zone Areal Extent (km2) Interpolation Observations Data Analysis Workshop Steering Committee Trevor Meckley, Alan Lewitus, A White Paper by the Steering Committee of the: Dave Scheurer, Dave Hilmer NOAA National Ocean Service, National 6th Annual NOAA/NGI Hypoxia Research Centers of Coastal Ocean Science Coordination Workshop: Establishing a Steve Ashby Cooperative Hypoxic Zone Monitoring Program Northern Gulf Institute convened by the NOAA National Centers for Steve DiMarco Texas A&M University Coastal Ocean Science and Northern Gulf Institute Steve Giordano on 12-13 September 2016 at the Mississippi State NOAA National Marine Fisheries Service University Science and Technology Center at Rick Greene NASA's Stennis Space Center in Mississippi. EPA Office of Research and Development Stephan Howden University of Southern Mississippi Barb Kirkpatrick Gulf of Mexico Coastal Ocean Observing System Troy Pierce EPA Gulf of Mexico Program Nancy Rabalais Louisiana Universities Marine Consortium Rick Raynie Louisiana Coastal Protection and Restoration Authority Mike Woodside USGS National Water Quality Program Abstract The Gulf of Mexico Hypoxia Monitoring Strategy is a resource to inform the proceedings of the 6th Annual NOAA/NGI Hypoxia Research Coordination Workshop: Establishing a Cooperative Hypoxic Zone Monitoring Program. It provides a framework for a cooperative hypoxia monitoring program based on programmatic and financial requirements that are designed to meet management needs. The Monitoring Strategy includes sections on management drivers, current monitoring capabilities and gaps, and projected programmatic, data, and financial requirements based on the input of multiple partners and the responses from a survey of modelers currently applying deterministic 3D time variable models to Gulf hypoxia assessment and prediction. -
Chesapeake Bay Restoration: Background and Issues for Congress
Chesapeake Bay Restoration: Background and Issues for Congress Updated August 3, 2018 Congressional Research Service https://crsreports.congress.gov R45278 SUMMARY R45278 Chesapeake Bay Restoration: Background and August 3, 2018 Issues for Congress Eva Lipiec The Chesapeake Bay (the Bay) is the largest estuary in the United States. It is Analyst in Natural recognized as a “Wetlands of International Importance” by the Ramsar Convention, a Resources Policy 1971 treaty about the increasing loss and degradation of wetland habitat for migratory waterbirds. The Chesapeake Bay estuary resides in a more than 64,000-square-mile watershed that extends across parts of Delaware, Maryland, New York, Pennsylvania, Virginia, West Virginia, and the District of Columbia. The Bay’s watershed is home to more than 18 million people and thousands of species of plants and animals. A combination of factors has caused the ecosystem functions and natural habitat of the Chesapeake Bay and its watershed to deteriorate over time. These factors include centuries of land-use changes, increased sediment loads and nutrient pollution, overfishing and overharvesting, the introduction of invasive species, and the spread of toxic contaminants. In response, the Bay has experienced reductions in economically important fisheries, such as oysters and crabs; the loss of habitat, such as underwater vegetation and sea grass; annual dead zones, as nutrient- driven algal blooms die and decompose; and potential impacts to tourism, recreation, and real estate values. Congress began to address ecosystem degradation in the Chesapeake Bay in 1965, when it authorized the first wide-scale study of water resources of the Bay. Since then, federal restoration activities, conducted by multiple agencies, have focused on reducing pollution entering the Chesapeake Bay, restoring habitat, managing fisheries, protecting sub-watersheds within the larger Bay watershed, and fostering public access and stewardship of the Bay. -
Marine Nature Conservation in the Pelagic Environment: a Case for Pelagic Marine Protected Areas?
Marine nature conservation in the pelagic environment: a case for pelagic Marine Protected Areas? Susan Gubbay September 2006 Contents Contents......................................................................................................................................... 1 Executive summary....................................................................................................................... 2 1 Introduction........................................................................................................................... 4 2 The pelagic environment....................................................................................................... 4 2.1 An overview...................................................................................................................... 4 2.2 Characteristics of the pelagic environment ....................................................................... 5 2.3 Spatial and temporal structure in the pelagic environment ............................................... 6 2.4 Marine life....................................................................................................................... 10 3 Biodiversity conservation in the pelagic environment........................................................ 12 3.1 Environmental concerns.................................................................................................. 12 3.2 Legislation, policy and management tools...................................................................... 15 -
PESHTIGO RIVER DELTA Property Owner
NORTHEAST - 10 PESHTIGO RIVER DELTA WETLAND TYPES Drew Feldkirchner Floodplain forest, lowland hardwood, swamp, sedge meadow, marsh, shrub carr ECOLOGY & SIGNIFICANCE supports cordgrass, marsh fern, sensitive fern, northern tickseed sunflower, spotted joe-pye weed, orange This Wetland Gem site comprises a very large coastal • jewelweed, turtlehead, marsh cinquefoil, blue skullcap wetland complex along the northwest shore of Green Bay and marsh bellflower. Shrub carr habitat is dominated three miles southeast of the city of Peshtigo. The wetland by slender willow; other shrub species include alder, complex extends upstream along the Peshtigo River for MARINETTE COUNTY red osier dogwood and white meadowsweet. Floodplain two miles from its mouth. This site is significant because forest habitats are dominated by silver maple and green of its size, the diversity of wetland community types ash. Wetlands of the Peshtigo River Delta support several present, and the overall good condition of the vegetation. - rare plant species including few-flowered spikerush, The complexity of the site – including abandoned oxbow variegated horsetail and northern wild raisin. lakes and a series of sloughs and lagoons within the river delta – offers excellent habitat for waterfowl. A number This Wetland Gem provides extensive, diverse and high of rare animals and plants have been documented using quality wetland habitat for many species of waterfowl, these wetlands. The area supports a variety of recreational herons, gulls, terns and shorebirds and is an important uses, such as hunting, fishing, trapping and boating. The staging, nesting and stopover site for many migratory Peshtigo River Delta has been described as the most birds. Rare and interesting bird species documented at diverse and least disturbed wetland complex on the west the site include red-shouldered hawk, black tern, yellow shore of Green Bay. -
A Synthesis of Information I
Outer Continental Shelf Environmental Assessment Program * A Synthesis of Information I U.S. DEPARTMENT OF COMMERCE U.S. DEPARTMENT OF THE INTEXIOR National Oceanic and Atmospheric Administration Minerals Management Service National Ocean Service Alaska OCS Region Office of Oceanography and Marine Assessment . .:.% y! Ocean Assessments Division ' t. CU ' k Alaska Office OCS Study, MMS 89-0081 . '.'Y. 4 3 --- NOTICES This report has been prepared as part of the U.S. Department bf Commerce, National Oceanic and Atmospheric Administration's Outer Continental Shelf Environmental Assessment Program, and approved for publication. The inter- pretation of data and opinions expressed in this document are those of the authors. Approval does not necessarily signify that the contents reflect the views and policies of the Department of Commerce or those of the Department of the Interior. The National Oceanic and Atmospheric Administration (NOAA) does not approve, recommend, or endorse any proprietary material mentioned in this publication. No reference shall be made to NOAA or to this publication in any advertising or sales promotion which would indicate or imply that NOAA approves, recommends, or endorses any proprietary product or proprietary material mentioned herein, or which has as its purpose or intent to cause directly or indirectly the advertised product to be used or purchased because of this publication. Cover: LandsatTMimage of the Yukon Delta taken on Julg 22, 1975, showing the thamal gradients resulting from Yukon River discharge. In this image land is dqicted in sesof red indicating warmer temperatures versus the dark blues (colder temperatures) of Bering Sea waters. Yukon River water, cooh than the surround- ing land but wanner than marine waters, is represented bg a light aqua blue. -
Marine Biodiversity and International Law: Instruments and Institutions That Can Be Used to Conserve Marine Biological Diversity Internationally
MARINE BIODIVERSITY AND INTERNATIONAL LAW: INSTRUMENTS AND INSTITUTIONS THAT CAN BE USED TO CONSERVE MARINE BIOLOGICAL DIVERSITY INTERNATIONALLY SUZANNE IUDICELLO* MARGARET LYTLE† I. INTRODUCTION ............................................................................. 124 A. What is Marine Biodiversity? ........................................ 124 B. The Threats to Marine Biodiversity ............................... 126 II. OVEREXPLOITATION ..................................................................... 127 A. International Framework for Fisheries Management .................................................................... 129 1. Early Efforts at Fishery Management ............... 130 2. The 1982 Convention on the Law of the Sea ................................................... 131 B. Regional Fishery Organizations and Agreements ........ 134 C. Additional International Agreements Protecting Marine Mammals, Birds and Other Wildlife................. 136 1. Marine Mammal Conventions .......................... 136 2. Protection of Migratory Birds ........................... 138 3. Conservation of Overexploited Wildlife .......... 140 D. Domestic Strategies for Conserving Marine Biodiversity Globally ...................................................... 141 1. Trade and Economic Measures ......................... 141 2. Direct Regulation ............................................... 143 III. ALTERATION OF THE PHYSICAL ENVIRONMENT .......................... 144 A. Coastal Development ..................................................... -
Policy Highlights Marine Protected Areas Economics, Management and Effective Policy Mixes
Marine Protected Areas Economics, Management and Effective Policy Mixes Policy HIGHLIGHTS Marine Protected Areas Economics, Management and Effective Policy Mixes Progress in expanding the coverage of marine protected areas is underway. With a push from the Sustainable Development Goals their global coverage is expected to increase even further. But their effectiveness is uneven. It is one thing to draw a line on a map – it is another to effectively design, site, monitor and enforce them. We are starting to understand what works and what doesn’t. Adaptive management and improvements over time will be essential if marine conservation and sustainable use objectives are to be met. Simon Upton – OECD Environment Director POLICY HI G HLI G H T Pressures on marine ecosystems from human activities are already severe and the often S competing demands for marine space and resources are projected to rise. Costs of poor ocean management practices include environmental and social costs that are often not factored into decision-making processes. This undermines the resilience of the ecosystems upon which we depend, for food, for income, but also other less visible life-support functions such as coastal protection, habitat provisioning and carbon sequestration. Marine protected areas are one of the policy instruments available to help ensure the conservation and sustainable use of our vast yet vulnerable ecosystems. While progress is being made towards increasing the global coverage of marine protected areas, significantly greater efforts are needed to ensure these are also being located in areas that are under threat and can therefore yield greatest environmental benefits, and that they are effectively managed. -
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. -
Zooplankton Community Response to Seasonal Hypoxia: a Test of Three Hypotheses
diversity Article Zooplankton Community Response to Seasonal Hypoxia: A Test of Three Hypotheses Julie E. Keister *, Amanda K. Winans and BethElLee Herrmann School of Oceanography, University of Washington, Box 357940, Seattle, WA 98195, USA; [email protected] (A.K.W.); [email protected] (B.H.) * Correspondence: [email protected] Received: 7 November 2019; Accepted: 28 December 2019; Published: 1 January 2020 Abstract: Several hypotheses of how zooplankton communities respond to coastal hypoxia have been put forward in the literature over the past few decades. We explored three of those that are focused on how zooplankton composition or biomass is affected by seasonal hypoxia using data collected over two summers in Hood Canal, a seasonally-hypoxic sub-basin of Puget Sound, Washington. We conducted hydrographic profiles and zooplankton net tows at four stations, from a region in the south that annually experiences moderate hypoxia to a region in the north where oxygen remains above hypoxic levels. The specific hypotheses tested were that low oxygen leads to: (1) increased dominance of gelatinous relative to crustacean zooplankton, (2) increased dominance of cyclopoid copepods relative to calanoid copepods, and (3) overall decreased zooplankton abundance and biomass at hypoxic sites compared to where oxygen levels are high. Additionally, we examined whether the temporal stability of community structure was decreased by hypoxia. We found evidence of a shift toward more gelatinous zooplankton and lower total zooplankton abundance and biomass at hypoxic sites, but no clear increase in the dominance of cyclopoid relative to calanoid copepods. We also found the lowest variance in community structure at the most hypoxic site, in contrast to our prediction. -
Hypoxia the Gulf of Mexico’S Summertime Foe
Louisiana Coastal Wetlands Planning, Protection and Restoration News September 2004 Number 26 HYPOXIA THE GULF OF MEXICO’S SUMMERTIME FOE More Nitrogen Upstream, Fewer Filters Downstream Caernarvon: A Case Study WaterMarks Interview: John Day, LSU www.lacoast.gov September 2004 Number 26 WaterMarks is published three times a Louisiana Coastal Wetlands Planning, Protection and Restoration News year by the Louisiana Coastal Wetlands Conservation and Restoration Task Force to communicate news and issues Contents of interest related to the Coastal Wetlands Planning, Protection and Restoration Act of 1990. This legislation 3 Hypoxia: funds wetlands enhancement projects The Gulf of Mexico’s Summertime Foe nationwide, designating approximately $50 million annually for work in More Nitrogen Upstream, Louisiana. The state contributes 6 Fewer Filters Downstream 15 percent of the total cost of the project. Can Wetlands Restoration 8 Revitalize Offshore Waters? Caernarvon: 10 A Case Study What Lies Ahead 12 for the Dead Zone? Please address all questions, comments and changes of address to: WaterMarks Interview: James D. Addison 14 John Day, LSU WaterMarks Editor New Orleans District US Army Corps of Engineers P.O. Box 60267 Special thanks to Doug Daigle, Mississippi River Basin Alliance; Dugan Sabins, New Orleans, LA 70160-0267 (504) 862-2201 Louisiana State Hypoxia Committee; Ken Teague, U.S. Environmental Protection Agency; and Robert Twilley, Louisiana State University, for their assistance with e-mail: this issue of WaterMarks. [email protected] For more information about Louisiana’s coastal wetlands and the efforts planned and under way to ensure their survival, check out these sites on the web: www.lacoast.gov www.btnep.org www.saveLAwetlands.org About the Cover Blue Runners, a common Gulf Subscribe species, have the ability to escape To receive WaterMarks, e-mail [email protected] from waters with low oxygen con- For current meetings, events, and other news concerning Louisiana’s coastal tent.