1 PILOT PROJECT SAND GROYNES DELFLAND COAST R. Hoekstra1
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Coastal Flood Defences - Groynes
Coastal Flood Defences - Groynes Coastal flood defences are key to protecting our coasts against flooding, which is when normally dry, low lying flat land is inundated by sea water. Hard engineering methods are forms of coastal flood defences which mitigate the risk of flooding and coastal erosion and the consequential effects. Hard Engineering Hard engineering methods are often used as a temporary measure to protect against coastal flooding as they are costly and only last for a relatively short amount of time before they require maintenance. However, they are very effective at protecting the coastline in the short-term as they are immediately effective as opposed to some longer term soft engineering methods. But they are often intrusive and can cause issues elsewhere at other areas along the coastline. Groynes are low lying wood or concrete structures which are situated out to sea from the shore. They are designed to trap sediment, dissipate wave energy and restrict the transfer of sediment away from the beach through long shore drift. Longshore drift is caused when prevailing winds blow waves across the shore at an angle which carries sediment along the beach.Groynes prevent this process and therefore, slow the process of erosion at the shore. They can also be permeable or impermeable, permeable groynes allow some sediment to pass through and some longshore drift to take place. However, impermeable groynes are solid and prevent the transfer of any sediment. Advantages and Disadvantages +Groynes are easy to construct. +They have long term durability and are low maintenance. +They reduce the need for the beach to be maintained through beach nourishment and the recycling of sand. -
Continental Shelf the Last Maritime Zone
Continental Shelf The Last Maritime Zone The Last Maritime Zone Published by UNEP/GRID-Arendal Copyright © 2009, UNEP/GRID-Arendal ISBN: 978-82-7701-059-5 Printed by Birkeland Trykkeri AS, Norway Disclaimer Any views expressed in this book are those of the authors and do not necessarily reflect the views or policies of UNEP/GRID-Arendal or contributory organizations. The designations employed and the presentation of material in this book do not imply the expression of any opinion on the part of the organizations concerning the legal status of any country, territory, city or area of its authority, or deline- ation of its frontiers and boundaries, nor do they imply the validity of submissions. All information in this publication is derived from official material that is posted on the website of the UN Division of Ocean Affairs and the Law of the Sea (DOALOS), which acts as the Secretariat to the Com- mission on the Limits of the Continental Shelf (CLCS): www.un.org/ Depts/los/clcs_new/clcs_home.htm. UNEP/GRID-Arendal is an official UNEP centre located in Southern Norway. GRID-Arendal’s mission is to provide environmental informa- tion, communications and capacity building services for information management and assessment. The centre’s core focus is to facili- tate the free access and exchange of information to support decision making to secure a sustainable future. www.grida.no. Continental Shelf The Last Maritime Zone Continental Shelf The Last Maritime Zone Authors and contributors Tina Schoolmeester and Elaine Baker (Editors) Joan Fabres Øystein Halvorsen Øivind Lønne Jean-Nicolas Poussart Riccardo Pravettoni (Cartography) Morten Sørensen Kristina Thygesen Cover illustration Alex Mathers Language editor Harry Forster (Interrelate Grenoble) Special thanks to Yannick Beaudoin Janet Fernandez Skaalvik Lars Kullerud Harald Sund (Geocap AS) Continental Shelf The Last Maritime Zone Foreword During the past decade, many coastal States have been engaged in peacefully establish- ing the limits of their maritime jurisdiction. -
Management of Coastal Erosion by Creating Large-Scale and Small-Scale Sediment Cells
COASTAL EROSION CONTROL BASED ON THE CONCEPT OF SEDIMENT CELLS by L. C. van Rijn, www.leovanrijn-sediment.com, March 2013 1. Introduction Nearly all coastal states have to deal with the problem of coastal erosion. Coastal erosion and accretion has always existed and these processes have contributed to the shaping of the present coastlines. However, coastal erosion now is largely intensified due to human activities. Presently, the total coastal area (including houses and buildings) lost in Europe due to marine erosion is estimated to be about 15 km2 per year. The annual cost of mitigation measures is estimated to be about 3 billion euros per year (EUROSION Study, European Commission, 2004), which is not acceptable. Although engineering projects are aimed at solving the erosion problems, it has long been known that these projects can also contribute to creating problems at other nearby locations (side effects). Dramatic examples of side effects are presented by Douglas et al. (The amount of sand removed from America’s beaches by engineering works, Coastal Sediments, 2003), who state that about 1 billion m3 (109 m3) of sand are removed from the beaches of America by engineering works during the past century. The EUROSION study (2004) recommends to deal with coastal erosion by restoring the overall sediment balance on the scale of coastal cells, which are defined as coastal compartments containing the complete cycle of erosion, deposition, sediment sources and sinks and the transport paths involved. Each cell should have sufficient sediment reservoirs (sources of sediment) in the form of buffer zones between the land and the sea and sediment stocks in the nearshore and offshore coastal zones to compensate by natural or artificial processes (nourishment) for sea level rise effects and human-induced erosional effects leading to an overall favourable sediment status. -
1 the Influence of Groyne Fields and Other Hard Defences on the Shoreline Configuration
1 The Influence of Groyne Fields and Other Hard Defences on the Shoreline Configuration 2 of Soft Cliff Coastlines 3 4 Sally Brown1*, Max Barton1, Robert J Nicholls1 5 6 1. Faculty of Engineering and the Environment, University of Southampton, 7 University Road, Highfield, Southampton, UK. S017 1BJ. 8 9 * Sally Brown ([email protected], Telephone: +44(0)2380 594796). 10 11 Abstract: Building defences, such as groynes, on eroding soft cliff coastlines alters the 12 sediment budget, changing the shoreline configuration adjacent to defences. On the 13 down-drift side, the coastline is set-back. This is often believed to be caused by increased 14 erosion via the ‘terminal groyne effect’, resulting in rapid land loss. This paper examines 15 whether the terminal groyne effect always occurs down-drift post defence construction 16 (i.e. whether or not the retreat rate increases down-drift) through case study analysis. 17 18 Nine cases were analysed at Holderness and Christchurch Bay, England. Seven out of 19 nine sites experienced an increase in down-drift retreat rates. For the two remaining sites, 20 retreat rates remained constant after construction, probably as a sediment deficit already 21 existed prior to construction or as sediment movement was restricted further down-drift. 22 For these two sites, a set-back still evolved, leading to the erroneous perception that a 23 terminal groyne effect had developed. Additionally, seven of the nine sites developed a 24 set back up-drift of the initial groyne, leading to the defended sections of coast acting as 1 25 a hard headland, inhabiting long-shore drift. -
Guidance for Flood Risk Analysis and Mapping
Guidance for Flood Risk Analysis and Mapping Coastal Notations, Acronyms, and Glossary of Terms May 2016 Requirements for the Federal Emergency Management Agency (FEMA) Risk Mapping, Assessment, and Planning (Risk MAP) Program are specified separately by statute, regulation, or FEMA policy (primarily the Standards for Flood Risk Analysis and Mapping). This document provides guidance to support the requirements and recommends approaches for effective and efficient implementation. Alternate approaches that comply with all requirements are acceptable. For more information, please visit the FEMA Guidelines and Standards for Flood Risk Analysis and Mapping webpage (www.fema.gov/guidelines-and-standards-flood-risk-analysis-and- mapping). Copies of the Standards for Flood Risk Analysis and Mapping policy, related guidance, technical references, and other information about the guidelines and standards development process are all available here. You can also search directly by document title at www.fema.gov/library. Coastal Notation, Acronyms, and Glossary of Terms May 2016 Guidance Document 66 Page i Document History Affected Section or Date Description Subsection Initial version of new transformed guidance. The content was derived from the Guidelines and Specifications for Flood Hazard Mapping Partners, Procedure Memoranda, First Publication May 2016 and/or Operating Guidance documents. It has been reorganized and is being published separately from the standards. Coastal Notation, Acronyms, and Glossary of Terms May 2016 Guidance Document 66 -
NJ Art Reef Publisher
Participating Organizations Alliance for a Living Ocean American Littoral Society Clean Ocean Action www.CleanOceanAction.org Arthur Kill Coalition Asbury Park Fishing Club Bayberry Garden Club Bayshore Saltwater Flyrodders Main Office Institute of Coastal Education Belford Seafood Co-op Belmar Fishing Club 18 Hartshorne Drive 3419 Pacific Avenue Beneath The Sea P.O. Box 505, Sandy Hook P.O. Box 1098 Bergen Save the Watershed Action Network Wildwood, NJ 08260-7098 Berkeley Shores Homeowners Civic Association Highlands, NJ 07732-0505 Cape May Environmental Commission Voice: 732-872-0111 Voice: 609-729-9262 Central Jersey Anglers Ocean Advocacy Fax: 732-872-8041 Fax: 609-729-1091 Citizens Conservation Council of Ocean County Since 1984 Clean Air Campaign [email protected] [email protected] Coalition Against Toxics Coalition for Peace & Justice Coastal Jersey Parrot Head Club Coast Alliance Communication Workers of America, Local 1034 Concerned Businesses of COA Concerned Citizens of Bensonhurst Concerned Citizens of COA Concerned Citizens of Montauk Dosil’s Sea Roamers Eastern Monmouth Chamber of Commerce Environmental Response Network Bill Figley, Reef Coordinator Explorers Dive Club Fisheries Defense Fund NJ Division of Fish and Wildlife Fishermen’s Dock Cooperative Fisher’s Island Conservancy P.O. Box 418 Friends of Island Beach State Park Friends of Liberty State Park Friends of Long Island Sound Port Republic, NJ 08241 Friends of the Boardwalk Garden Club of Englewood Garden Club of Fair Haven December 6, 2004 Garden Club of Long Beach Island Garden Club of Morristown Garden Club of Navesink Garden Club of New Jersey RE: New Jersey Draft Artificial Reef Plan Garden Club of New Vernon Garden Club of Oceanport Garden Club of Princeton Garden Club of Ridgewood VIA FASCIMILE Garden Club of Rumson Garden Club of Short Hills Garden Club of Shrewsbury Garden Club of Spring Lake Dear Mr. -
Mathematical Model of Groynes on Shingle Beaches
HR Wallingford Mathematical Model of Groynes on Shingle Beaches A H Brampton BSc PhD D G Goldberg BA Report SR 276 November 1991 Address:Hydraulics Research Ltd, wallingford,oxfordshire oxl0 gBA,United Kingdom. Telephone:0491 35381 Intemarional + 44 49135381 relex: g4gsszHRSwALG. Facstunile:049132233Intemarional + M 49132233 Registeredin EngtandNo. 1622174 This report describes an investigation carried out by HR Wallingford under contract CSA 1437, 'rMathematical- Model of Groynes on Shingle Beaches", funded by the Ministry of Agri-culture, Fisheries and Food. The departmental nominated. officer for this contract was Mr A J Allison. The company's nominated. project officer was Dr S W Huntington. This report is published on behalf of the Ministry of Agriculture, Fisheries and Food, but the opinions e>rpressed are not necessarily those of the Ministry. @ Crown Copyright 1991 Published by permission of the Controller of Her Majesty's Stationery Office Mathematical model of groSmes on shingle beaches A H Brampton BSc PhD D G Goldberg BA Report SR 276 November 1991 ABSTRACT This report describes the development of a mathematical model of a shingle beach with gro5mes. The development of the beach plan shape is calculated given infornation on its initial position and information on wave conditions just offshore. Different groyne profiles and spacings can be specified, so that alternative gro5me systems can be investigated. Ttre model includes a method for dealing with varying water levels as the result of tidal rise and fall. CONTENTS Page 1. INTRODUCTION I 2. SCOPEOF THE UODEL 3 2.t Model resolution and input conditions 3 2.2 Sediment transport mechanisms 6 2.3 Vertical distribution of sediment transport q 2.4 Wave transformation modelling L0 3. -
Nh-Connect-The-Coast-Report.Pdf
Connect THE Coast LINKING WILDLIFE ACROSS NEW HAMPSHIRE’S SEACOAST AND BEYOND Final Report: 10/31/2019 Authors: Peter Steckler and Dea Brickner-Wood Connect THE Coast LINKING WILDLIFE ACROSS NEW HAMPSHIRE’S SEACOAST AND BEYOND FINAL REPORT 10/31/2019 Authors Peter Steckler GIS & Conservation Project Manager The Nature Conservancy, New Hampshire Dea Brickner-Wood Coordinator Great Bay Resource Protection Partnership Cite plan as: Steckler, P and Brickner-Wood, D. 2019. Connect The Coast final report. The Nature Conservancy and the Great Bay Resource Protection Partnership. Concord, NH. Cover: Map of New Hampshire’s Coastal watershed, created by The Nature Conservancy. Table of Contents Acknowledgements ................................................................................................................................ i Executive Summary ............................................................................................................................... ii 1. Introduction .................................................................................................................................... 1 Project Area .............................................................................................................................. 1 Conservation Context ............................................................................................................... 3 Historic Context of Land Use in the Coastal Watershed ........................................................ 4 Current Connectivity Challenges -
Shoreline Stabilisation
Section 5 SHORELINE STABILISATION 5.1 Overview of Options Options for handling beach erosion along the western segment of Shelley Beach include: • Do Nothing – which implies letting nature take its course; • Beach Nourishment – place or pump sand on the beach to restore a beach; • Wave Dissipating Seawall – construct a wave dissipating seawall in front of or in lieu of the vertical wall so that wave energy is absorbed and complete protection is provided to the boatsheds and bathing boxes behind the wall for a 50 year planning period; • Groyne – construct a groyne, somewhere to the east of Campbells Road to prevent sand from the western part of Shelley Beach being lost to the eastern part of Shelley Beach; • Offshore Breakwater – construct a breakwater parallel to the shoreline and seaward of the existing jetties to dissipate wave energy before it reaches the beach; and • Combinations of the above. 5.2 Do Nothing There is no reason to believe that the erosion process that has occurred over at least the last 50 years, at the western end of Shelley Beach, will diminish. If the water depth over the nearshore bank has deepened, as it appears visually from aerial photographs, the wave heights and erosive forces may in fact increase. Therefore “Do Nothing” implies that erosion will continue, more structures will be threatened and ultimately damaged, and the timber vertical wall become undermined and fail, exposing the structures behind the wall to wave forces. The cliffs behind the wall will be subjected to wave forces and will be undermined if they are not founded on solid rock. -
Mapping the Canyon
Deep East 2001— Grades 9-12 Focus: Bathymetry of Hudson Canyon Mapping the Canyon FOCUS Part III: Bathymetry of Hudson Canyon ❒ Library Books GRADE LEVEL AUDIO/VISUAL EQUIPMENT 9 - 12 Overhead Projector FOCUS QUESTION TEACHING TIME What are the differences between bathymetric Two 45-minute periods maps and topographic maps? SEATING ARRANGEMENT LEARNING OBJECTIVES Cooperative groups of two to four Students will be able to compare and contrast a topographic map to a bathymetric map. MAXIMUM NUMBER OF STUDENTS 30 Students will investigate the various ways in which bathymetric maps are made. KEY WORDS Topography Students will learn how to interpret a bathymet- Bathymetry ric map. Map Multibeam sonar ADAPTATIONS FOR DEAF STUDENTS Canyon None required Contour lines SONAR MATERIALS Side-scan sonar Part I: GLORIA ❒ 1 Hudson Canyon Bathymetry map trans- Echo sounder parency ❒ 1 local topographic map BACKGROUND INFORMATION ❒ 1 USGS Fact Sheet on Sea Floor Mapping A map is a flat representation of all or part of Earth’s surface drawn to a specific scale Part II: (Tarbuck & Lutgens, 1999). Topographic maps show elevation of landforms above sea level, ❒ 1 local topographic map per group and bathymetric maps show depths of land- ❒ 1 Hudson Canyon Bathymetry map per group forms below sea level. The topographic eleva- ❒ 1 Hudson Canyon Bathymetry map trans- tions and the bathymetric depths are shown parency ❒ with contour lines. A contour line is a line on a Contour Analysis Worksheet map representing a corresponding imaginary 59 Deep East 2001— Grades 9-12 Focus: Bathymetry of Hudson Canyon line on the ground that has the same elevation sonar is the multibeam sonar. -
Coastal Upwelling in the Eastern Gulf of California
OCEANOLOGICA ACTA · VOL. 23 – N° 6 Coastal upwelling in the eastern Gulf of California Salvador-Emilio LLUCH-COTA * Centro de Investigaciones Biolo´gicas del Noroeste, S.C. PO Box 128 La Paz, BCS, Me´xico 23000 Received 11 May 1999; revised 8 December 1999; accepted 13 December 1999 Abstract – Understanding and quantifying upwelling is of great importance for marine resource management. Direct measurement of this process is extremely difficult and observed time-series do not exist. However, proxies are commonly derived from different data; most commonly wind-derived. A local wind-derived coastal upwelling index (CUI) is reported for the period 1970–1996 and is considered representative for the eastern central Gulf of California, an important fishing area where no proxies exist. The index is well related to pigment concentration distribution, surface water temperature, and population dynamics of important fish resources over the seasonal time-scale. There is a biological response to ENSO activity not reflected by this index, indicating that improvement of biological enrichment forecasting also requires water column structure input. A clearly increasing seasonal amplitude signal is detected in the coastal upwelling index and sea surface temperature since the mid 1970s. Understanding the nature of these long-term trends, the incorporation of remote tropical ocean signals into the enrichment proxy, the dynamics of atmosphere and ocean, and the biological responses are major challenges to the proper management of fish resources in the Gulf of California. upwelling / Gulf of California / seasonality / climate change Re´sume´–Upwelling coˆtier dans l’est du golfe de Californie. Comprendre et e´valuer le phe´nome`ne d’upwelling est tre`s important pour la gestion des ressources marines. -
The Case-Study of Fongafale, Atool of Funafuti
Shoreline of human-impacted coralline atolls: need for a concerted management. The case-study of Fongafale, atoll of Funafuti, Tuvalu Caroline Rufin The atoll of Funafuti (Tuvalu archipelago) is located in the South Pacific Ocean at latitude 8.31° South and longitude 179.13° East (Figure 1). According to its morphology, Fongafale island (atoll of Funafuti) can be split into three distinct geographical areas, i.e. the northern, central and southern parts. The present study deals with the central part, which results from the deposition of sediments from the two other areas following North and South longshore drifts. Marshall •• Islands, 1o·N Kiribati! . ~ ~· ... ' ... .. ·. ~ Samoa .. o_. •• Vanuatu b •! ; . b\ Fiji ,::::1 . ~ 0 Tonga .. ' '· : .... 2o·s New .. ~.'•. ' •• Caledon~. • • • 100· 110· 180' 170' 160"W Source : from Mclean et Hosking. 1991 Figure 1 Localisation of Tuvalu within the Pacific Bassin. 436 Coral reefs in the Pacifie: Status and monitoring, Resources and management Through the example of Fongafale island, the present study is aimed at thinking about the manage ment of low coralline islands confronted with erosion problems most often in relation with excessive coastal planning. This thought will be developed in terms of global geography while taking into account ail the environmental conditions. Our purpose will be not to demonstrate which of the two factors, Man or Nature, is the more disturb ing. However, from the analysis of our data set it is clear that the contribution of the former is greater than that of the latter. We will first draw a schedule of Fongafale lagoon shoreline from aerial pictures and topographical readings; it will be essential to understand the environmental problems which this atoll is submitted to.