Survey of Temperature Variation Effect on Underwater Acoustic Wireless Transmission Ghada ZAÏBI*, Nejah NASRI*, Abdennaceur KACHOURI* and Mounir SAMET *

Total Page:16

File Type:pdf, Size:1020Kb

Survey of Temperature Variation Effect on Underwater Acoustic Wireless Transmission Ghada ZAÏBI*, Nejah NASRI*, Abdennaceur KACHOURI* and Mounir SAMET * SETIT 2009 5th International Conference: Sciences of Electronic, Technologies of Information and Telecommunications March 22-26, 2009 – TUNISIA Survey Of Temperature Variation Effect On Underwater Acoustic Wireless Transmission Ghada ZAÏBI*, Nejah NASRI*, Abdennaceur KACHOURI* and Mounir SAMET * * Laboratory of Electronics and Technologies of Information (LETI) National School of Engineers of Sfax B.P.W, 3038 Sfax, Tunisia [email protected] [email protected] [email protected] [email protected] Abstract: In acoustic channel it is known that low available bandwidth, highly varying multipath, large propagation delays, noise and physical channel properties variation, in addition to the power consumption restrict the efficiency of underwater wireless acoustic systems. The physical characteristics of Mediterranean channel such as depth, salinity and especially temperature influence the acoustic signal attenuation, the SNR level, error ratio and the signal bandwidth. It seems to be crucial to introduce these parameters in the underwater channel model of the underwater wireless communication network. The goal of this paper is to highlight the impact of the temperature variation at shallow sea on the acoustic signal attenuation and error ratio and explain the relationship between temperature and SNR as well as the optimal frequency of the transmitted signal. Key words: optimal frequency, SNR, temperature, underwater acoustic channel. as temperature, salinity and depth variation [SOZ 00], [WON 05], [COP 82]. INTRODUCTION This article characterizes the underwater channel In spite of the use of electromagnetic wave, especially and presents its physical characteristics survey as well radio wave in the mobile radio communications, its as its parameters variation effect on the acoustic signal propagation in underwater environment is limited in attenuation. We establish the relationship between few meters. SNR and temperature values and finally we evaluate They are rapidly attenuated and require an important temperature changes effect on image quality. transmission power as well as large antennae. On the other hand, acoustic communications showed the best performances compared to the electromagnetic waves. 1. Description of underwater channel Thus, underwater wireless communications are The underwater channel is an intermittent channel. established by acoustic wave but remain far from an It is characterized by its limited bandwidth, long ideal communication. propagation delays and frequency selectivity The transmission of a reliable underwater acoustic This Disturbance and characteristics of the signal with the least distortions and the minimum underwater channel are represented by three blocks. emission power is attracting increasing interest from researchers considering the unfavourable conditions of In fact, the noise of the underwater is modelled by the the shallow underwater environment, as well as the AWGN channel. The Rayleigh channel represents the problems encountered when providing the system with multipath delay, fading and Doppler frequency shift. energy [AKY 05]. Moreover, adding an attenuation block is necessary to Several alternatives try to improve signal’s quality model transmission losses. Variables f, d, p are (signal to noise ratio, inter-symbols interferences respectively frequency, distance and physical (ISI)) and reduce power consumption of the characteristics (figure 1). underwater channel by modelling a suitable underwater transmission system neglecting the physical specifications of the underwater channel such - 1 - SETIT2009 Table 1. Average values of temperature (winter- summer) and salinity of the Mediterranean Figure 1. Underwater channel model. 1.1. Physical characteristics of the underwater channel In underwater acoustic communication, the well known of the underwater channel will improve the modelling of the underwater acoustic system. The characteristics of the ocean or sea water such as salinity, temperature, density, and current velocity do not vary smoothly with depth, but in a discontinuous fashion. They remain almost constant within certain 1.1.2. Attenuation of the acoustic wave in marine layers and change rapidly in passing from one layer to environment another. The thickness of these layers varies from tens The sound propagation in sea water leads to of centimetres to tens of meters. acoustic signal attenuation. This attenuation is due to In fact, this discontinuity of water layers has a two effects: geometrical considerations like diffusion deep effect on the transmission of an acoustic signal and non geometrical effect like absorption. by increasing or decreasing the attenuation value. The signal attenuation is given by the following 1.1.1. Mediterranean sea formula (1): The Mediterranean Sea is the crossroad of the x(f ) three continents: Europe, Asia and Africa. It is a deep A(x) x k10 10 sea. Its average depth is about 1500 meters and its (1) maximum depth is 5121 meters (narrow trench in the south of the Cape Matapan (Greece)). Mediterranean sea-beds form a chaotic zone. They are Where k represents the spreading factor (k = 1 for characterized by variable depths (siculo-Tunisian cylindrical spreading, k = 1.5 is the practical value and threshold (400m); Gibraltar (less than 100m); the k = 2 for spherical spreading) and β(f) is the Turkish straits threshold (less than 50m)) [SIM 02]. absorption coefficient in dB/Km (for x is the distance between 2 nodes on Km) . The temperature and the salinity of Mediterranean water (from Western to Eastern Mediterranean) The absorption coefficient is chosen for undergo fluctuations which are influenced by the frequencies between 3 KHz and 0.5 MHz, according currents and the depths [ERI 65]. Indeed, water to Marsh and Schulkin empirical formula [STO 06], surface temperature varies between 10 and 30 °C, and as: is stabilized in-depth in an average value of 13 °C. These values are different from surface Atlantic S.A.f .f 2 B.f 2 ( f ) 8.68.103 T 1 6.54.104 P temperatures which reach 4 °C and even less. 2 2 (2) fT f fT The rate of salinity of the Mediterranean varies between 36 ‰ (in the west) and 39 ‰ (in the east) For f in KHz, A = 2.34.10-6, B = 3.38.10-6, S is the [BET 05] and the average rate is close to 37,5 ‰. salinity (‰), P is the hydrostatic pressure [kg/cm²], Its value oscillates around 36 ‰ close to the 6-1520/(T+273) and fT = 21.9.10 is the relaxation frequency Gibraltar Straits where water marries by the currents (kHz) with T is the temperature between 0 and 30 °C. with those of the Atlantic and it is between 38 and It takes into account the variation of salinity, depth 39 ‰ at the Gulf of Gabes (minor Syrte). and temperature which characterise absorption due to The average values of the temperature (winter- the MgSO4 relaxation. It depends also on the shear summer) and salinity measured at various depths (m) viscosity and volume viscosity in the frequency band for several places of the Mediterranean Sea is 100 Hz -100 Khz. illustrated by the following table [ZEN 02]. Both expressions (1) and (2) of signal attenuation and absorption coefficient are used to extract how physical sea water characteristics attenuate the propagated signal. - 2 - SETIT2009 2. Sea water characteristics impact on the compensating its effect. Signal attenuation For the other characteristics, their impact is less In this subsection, the focus was on the important than temperature especially for the temperature variation especially at shallow sea and its Mediterranean Sea because it’s not as deep as the impact on the acoustic signal attenuation. Indeed, the Atlantic Ocean, for example. The attenuation research showed the parameters which increase the difference between salinity extremes is about 5.10-2 ‰ temperature influence on signal attenuation when at 200 m depth, 1 Km distance, average temperature propagated in shallow water. and 10 KHz frequency. Table 2(a) shows that for two nodes separated by In the next subsection, the underwater channel 1Km distance and placed at 200 m depth, with an characteristics chosen are 10 KHz as frequency, 200m average salinity, attenuation variation is about 0.46 dB as depth, an average salinity (37.5 ‰) and temperature for 10 KHz signal frequency at the extreme (13 °C). Mediterranean sea temperature values. Table 2(a). Attenuation variations for different 3. Relationship between the environment temperatures at 1 Km and 10 KHz. temperature and SNR 3.1. Ambient noise The ambient noise is the background noise of the ocean due to four causes: turbulence, shipping activities, waves and thermal noise [STO 06], [LUR 98]. It can be described by Gaussian statistics and a continuous power spectral density (p.s.d). The following formulae present the p.s.d of the four noise sources in dB re µ Pa per Hz as a frequency If the distance between the two nodes increases, function in KHz: example 5 Km (table 2(b)), then the temperature influence is a linear function and the attenuation 10 log(Nt (f)) 17 30(log(f)) (3) difference reaches 2.3 dB at the same frequency. 10 log(Ns (f )) 40 20(s 0.5) 26 log(f ) Table 2(b). Attenuation variations for different [60 log(f 0.03)] (4) temperatures at 5 Km and 10 KHz. 1 2 10 log(N w (f )) 50 7.5w 20 log(f ) [40 log(f 0.4)] (5) 10 log(Na (f)) 15 20 log(f) (6) In the second expression, shipping activity factor s varies between 0 and 1. The wind speed is w in m/s. The total spectral density p.s.d of the ambient noise is In addition, if we use high signal frequencies, for the combination of its four components: example 50 KHz (table 2(c)) then the variation of attenuation is about 7.65 dB. N(f) N (f) N (f) N (f) N (f) (7) Table 2(c). Attenuation variations for different t s w a temperature at 1 Km and 50 KHz. 3.2.
Recommended publications
  • Undersea Park America's First
    KEY LARGO CORAL REEF America's First i~jl Undersea Park By CHARLES M. BROOKFIELD Photographs by JERRY GREENBERG ,I, ,.;;!' MO ST within sight of the oceanside ~Ii palaces of Miami Beach, a pencil-thin il- Achain of islands begins its 221-mile sweep southwest to the Dry Tortugas. Just offshore, paralleling the scimitar plor%E 6 II curve of these Florida Keys, lies an under­ qy-q sea rampart of exquisite beauty-a living coral reef, the only one of its kind in United States continental waters. Brilliant tropical ~". fish dart about its multicolored coral gardens. Part of the magnificent reef, a segment rough­ ly 21 nautical miles long by 4 wide, off Key Largo, has been .dedicated as America's first undersea park. I know this reef intimately. For more than 30 years I have sailed its warm, clear waters and probed its shifting sands and bizarre for­ mations in quest of sunken ships and their treasure of artifacts. ',." Snorkel diver (opposite, right) glides above brain coral into a fantastic underseascape of elkhorn and staghom in the new preserve off Key Largo, Florida 1~¥~-4 - ce il\ln ·ii Here is a graveyard of countless brave sail­ uncover this interesting fact until two 'years 'ti: ing ships, Spanish galleons, English men-ot­ ago, when I learned that the Willche~lel"s ~j~ war, pirate vessels, and privateers foundered log had been saved. Writing to the Public h~l on the reefs hidden fangs. In the 19th century Record Office in London, I obtained photo­ alone, several hundred vessels met death static-copies of the last few pages.
    [Show full text]
  • Accuracy Assessment of Underwater Photogrammetric Three Dimensional Modelling for Coral Reefs
    The International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Volume XLI-B5, 2016 XXIII ISPRS Congress, 12–19 July 2016, Prague, Czech Republic ACCURACY ASSESSMENT OF UNDERWATER PHOTOGRAMMETRIC THREE DIMENSIONAL MODELLING FOR CORAL REEFS T. Guo a, *, A. Capra b, M. Troyer a, A. Gruen a, A. J. Brooks c, J. L. Hench d, R. J. Schmittc, S. J. Holbrook c, M. Dubbini e a Theoretical Physics, ETH Zurich, 8093 Zurich, Switzerland - (taguo, troyer)@phys.ethz.ch, [email protected] b Dept. of Engineering “Enzo Ferrari”, University of Modena and Reggio Emilia, via Pietro Vivarelli 10/1, 41125 Modena, Italy – [email protected] c Marine Science Institute, University of California, Santa Barbara. Santa Barbara, California 93106-6150, USA – [email protected], (schmitt, holbrook)@lifesci.ucsb.edu d Nicholas School of the Environment, Duke University, Beaufort, NC, USA - [email protected] e Dept. of History Culture Civilization – Headquarters of Geography, University of Bologna, via Guerrazzi 20, 40125 Bologna, Italy [email protected] Commission V, WG V/5 KEY WORDS: Photogrammetry, Underwater 3D Modelling, Accuracy Assessment, Calibration, Point Clouds, Coral Reefs, Coral Growth, Moorea ABSTRACT: Recent advances in automation of photogrammetric 3D modelling software packages have stimulated interest in reconstructing highly accurate 3D object geometry in unconventional environments such as underwater utilizing simple and low-cost camera systems. The accuracy of underwater 3D modelling is affected by more parameters than in single media cases. This study is part of a larger project on 3D measurements of temporal change of coral cover in tropical waters.
    [Show full text]
  • Ecological and Socio-Economic Impacts of Dive
    ECOLOGICAL AND SOCIO-ECONOMIC IMPACTS OF DIVE AND SNORKEL TOURISM IN ST. LUCIA, WEST INDIES Nola H. L. Barker Thesis submittedfor the Degree of Doctor of Philosophy in Environmental Science Environment Department University of York August 2003 Abstract Coral reefsprovide many servicesand are a valuableresource, particularly for tourism, yet they are suffering significant degradationand pollution worldwide. To managereef tourism effectively a greaterunderstanding is neededof reef ecological processesand the impactsthat tourist activities haveon them. This study explores the impact of divers and snorkelerson the reefs of St. Lucia, West Indies, and how the reef environmentaffects tourists' perceptionsand experiencesof them. Observationsof divers and snorkelersrevealed that their impact on the reefs followed certainpatterns and could be predictedfrom individuals', site and dive characteristics.Camera use, night diving and shorediving were correlatedwith higher levels of diver damage.Briefings by dive leadersalone did not reducetourist contactswith the reef but interventiondid. Interviewswith tourists revealedthat many choseto visit St. Lucia becauseof its marineprotected area. Certain site attributes,especially marine life, affectedtourists' experiencesand overall enjoyment of reefs.Tourists were not alwaysable to correctly ascertainabundance of marine life or sedimentpollution but they were sensitiveto, and disliked seeingdamaged coral, poor underwatervisibility, garbageand other tourists damagingthe reef. Some tourists found sitesto be
    [Show full text]
  • Overview of the Impacts of Anthropogenic Underwater Sound in the Marine Environment
    Overview of the impacts of anthropogenic underwater sound in the marine environment Biodiversity Series 2009 Overview of the impacts of anthropogenic underwater sound in the marine environment OSPAR Convention Convention OSPAR The Convention for the Protection of the La Convention pour la protection du milieu Marine Environment of the North-East Atlantic marin de l'Atlantique du Nord-Est, dite (the “OSPAR Convention”) was opened for Convention OSPAR, a été ouverte à la signature at the Ministerial Meeting of the signature à la réunion ministérielle des former Oslo and Paris Commissions in Paris anciennes Commissions d'Oslo et de Paris, on 22 September 1992. The Convention à Paris le 22 septembre 1992. La Convention entered into force on 25 March 1998. It has est entrée en vigueur le 25 mars 1998. been ratified by Belgium, Denmark, Finland, La Convention a été ratifiée par l'Allemagne, France, Germany, Iceland, Ireland, la Belgique, le Danemark, la Finlande, Luxembourg, Netherlands, Norway, Portugal, la France, l’Irlande, l’Islande, le Luxembourg, Sweden, Switzerland and the United Kingdom la Norvège, les Pays-Bas, le Portugal, and approved by the European Community le Royaume-Uni de Grande Bretagne and Spain. et d’Irlande du Nord, la Suède et la Suisse et approuvée par la Communauté européenne et l’Espagne. 2 OSPAR Commission, 2009 Acknowledgements Author list (in alphabetical order) Thomas Götz Scottish Oceans Institute, East Sands University of St Andrews St Andrews, Fife KY16 8LB [email protected] Module 2, 8 Gordon Hastie SMRU Limited New Technology Centre North Haugh St Andrews, Fife KY16 9SR [email protected] Module 2, 8 Leila T.
    [Show full text]
  • 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.
    [Show full text]
  • Review of Human Physiology in the Underwater Environment
    Available online at www.ijmrhs.com cal R edi ese M ar of c l h a & n r H u e o a J l l t h International Journal of Medical Research & a S n ISSN No: 2319-5886 o c i t i Health Sciences, 2019, 8(8): 117-121 e a n n c r e e t s n I • • IJ M R H S Review of Human Physiology in the Underwater Environment Oktiyas Muzaky Luthfi1,2* 1 Marine Science University of Brawijaya, Malang, Indonesia 2 Fisheries Diving School, University of Brawijaya, Malang, Indonesia *Corresponding e-mail: [email protected] ABSTRACT Since before centuries, human tries hard to explore underwater and in 1940’s human-introduced an important and revolutionary gear i.e. scuba that allowed human-made long interaction in the underwater world. Since diving using pressure gas under pressure environment, it should be considered to remember gas law (Boyle’s law). The gas law gives a clear understanding of physiological consequences related to diving diseases such as barotrauma or condition in which tissue or organ is damage due to gas pressure. The organ which has direct effect related to compression and expansion of gas were lungs, ear, and sinus. These organs were common and potentially fatigue injury for a diver. In this article we shall review the history of scuba diving, physical stress caused underwater environment, physiology adaptation of lung, ear, and sinus, and diving disease. Keywords: Barotrauma, Boyle’s law, Scuba, Barine, Physical stress INTRODUCTION The underwater world is a place where many people dream to explore it.
    [Show full text]
  • 10 Ways Divers Can Help
    iver n Ways a D Can Protect Te the Underwater Environment 1. Dive carefully to protect fragile aquatic ecosystems 6. Be an ecotourist Many aquatic organisms are delicate and can be harmed by Make informed decisions when selecting a destination and the bump of a camera, the swipe of a fin or even the gentle choose Project AWARE Environmental Operators or other touch of a hand. Some aquatic organisms like corals grow facilities dedicated to sustainable business practices. Obey very slowly and breaking even a small piece can destroy all local laws and regulations and understand your effect on decades of growth. By being careful you can prevent long- the environment. Don’t collect souvenirs like corals or shells. term damage to magnificent dive sites. Instead, take underwater photos and follow Project AWARE’s 10 Tips for Underwater Photographers. 2. Be aware of your body and equipment placement when diving 7. Respect underwater cultural heritage Keep your gauges and alternate air source secured so they Divers are privileged to access dive sites that are part of our don’t drag over the reef or other vital habitat. Control your cultural heritage and maritime history. Wrecks can also serve buoyancy, taking care not to touch fragile organisms with as important habitats for fish and other aquatic life. Help your body or equipment. You can do your part and prevent preserve these sites for future generations by obeying local injury to aquatic life every time you dive. laws, diving responsibly and treating wrecks with respect. 3. Keep your dive skills sharp 8.
    [Show full text]
  • Researching the Great Barrier Reef Supporting Virtual Reef Diver, Supports Monitoring Our Reefs! Virtual Reef Diver
    SUPPORTING VIRTUAL REEF DIVER, SUPPORTS MONITORING OUR REEFS! The more images we have of the reef and the more people who classify each of these images, the more information can be extracted from the data during the modelling process. RESEARCHING THE GREAT BARRIER REEF The Great Barrier Reef was designated a World Heritage Area in 1981 and is the largest coral reef ecosystem on earth, with over 2,900 coral reefs spread over approximately 348,000 km2. This biologically diverse underwater environment supports over 1,500 fish and 600 coral species, alongside thousands of molluscs, marine ma mals, sea turtles and birds. An enormous amount of effort is invested in monitoring the Great Barrier Reef, with dozens of publicly and privately funded monitoring programs in place, run by research institutions, government agencies, reef-based industries, citizen-science groups, and traditional owners. However, no single organisation can monitor the entire Great Barrier Reef on its own. The motivation for the Virtual Reef Diver project was to find a way to make use of all the existing monitoring data VIRTUAL REEF DIVER collected by these organisations, and to look for other innovative ways to obtain new data in a cost-effective manner. Institute for Future Environments QUT Gardens Point Campus 2 George Street, Brisbane QLD 4000 Australia +61 412 160 067 [email protected] www.virtualreef.org.au WWW.VIRTUALREEF.ORG.AU Monitorning the Great Barrier Reef © 2018. Produced by Virtual Reef Diver. Queensland University of Technology Photos: Trevor Smith, Terry through education, outreach, and Cummins and Virtual Reef Diver. monitoring.
    [Show full text]
  • An Upwelling Radiance Distribution Camera System, NURADS
    An Upwelling Radiance Distribution Camera System, NURADS Kenneth J. Voss and Albert L. Chapin Physics Department, University of Miami, Coral Gables, Fl. 33124 [email protected] Abstract: We have built a new instrument to measure the in-water spectral upwelling radiance distribution. This instrument measures the radiance distribution at six wavelengths and obtains a complete suite of measurements (6 spectral data images with associated dark images) in approximately 2 minutes (in clear water). This instrument is much smaller than previous instruments (0.3 m in diameter and 0.3 m long), decreasing the instrument self-shading. It also has improved performance resulting from enhanced sensor sensitivity and a more subtle lens rolloff effect. We describe the instrument, its characterization, and show data examples from both clear and turbid water. ©2004 Optical Society of America OCIS codes: References and Links 1. Tyler, J.E. 1960. Radiance distribution as a function of depth in an underwater environment. Bull. Scripps Inst. Oceanogr. 7: 363-41. 2. Aas, E., and N. K. Hojerslev. 1999. Analysis of underwater radiance distribution observations: apparent optical properties and analytical functions describing the angular radiance distributions. J. Geophys. Res. 104: 8015 - 8024. 3. Smith, R. C., R. W. Austin and J. E. Tyler. 1970. An oceanographic radiance distribution camera system. Appl. Opt. 9: 2015-2022. 4. Voss, K. J. 1989. Electro-optic camera system for measurement of the underwater radiance distribution. Optical Engineering. 28: 241-247. 5. Voss, K. J. and A. L. Chapin. 1992. Next generation in-water radiance distribution camera system. Proc. Soc. Photo-Optical Instrumentation Engineers, 1759: 384 - 387.
    [Show full text]
  • Assessment of the Effects of Noise and Vibration from Offshore Wind Farms on Marine Wildlife
    ASSESSMENT OF THE EFFECTS OF NOISE AND VIBRATION FROM OFFSHORE WIND FARMS ON MARINE WILDLIFE ETSU W/13/00566/REP DTI/Pub URN 01/1341 Contractor University of Liverpool, Centre for Marine and Coastal Studies Environmental Research and Consultancy Prepared by G Vella, I Rushforth, E Mason, A Hough, R England, P Styles, T Holt, P Thorne The work described in this report was carried out under contract as part of the DTI Sustainable Energy Programmes. The views and judgements expressed in this report are those of the contractor and do not necessarily reflect those of the DTI. First published 2001 i © Crown copyright 2001 EXECUTIVE SUMMARY Main objectives of the report Energy Technology Support Unit (ETSU), on behalf of the Department of Trade and Industry (DTI) commissioned the Centre for Marine and Coastal Studies (CMACS) in October 2000, to assess the effect of noise and vibration from offshore wind farms on marine wildlife. The key aims being to review relevant studies, reports and other available information, identify any gaps and uncertainties in the current data and make recommendations, with outline methodologies, to address these gaps. Introduction The UK has 40% of Europe ’s total potential wind resource, with mean annual offshore wind speeds, at a reference of 50m above sea level, of between 7m/s and 9m/s. Research undertaken by the British Wind Energy Association suggests that a ‘very good ’ site for development would have a mean annual wind speed of 8.5m/s. The total practicable long-term energy yield for the UK, taking limiting factors into account, would be approximately 100 TWh/year (DTI, 1999).
    [Show full text]
  • The Drone Revolution of Shark Science: a Review
    drones Review The Drone Revolution of Shark Science: A Review Paul A. Butcher 1,2,* , Andrew P. Colefax 3, Robert A. Gorkin III 4 , Stephen M. Kajiura 5 , Naima A. López 6 , Johann Mourier 7 , Cormac R. Purcell 8,9 , Gregory B. Skomal 10, James P. Tucker 2, Andrew J. Walsh 3,8, Jane E. Williamson 11 and Vincent Raoult 12 1 NSW Department of Primary Industries, National Marine Science Centre, P.O. Box 4321, Coffs Harbour, NSW 2450, Australia 2 School of Environment, Science and Engineering, Southern Cross University, National Marine Science Centre, Coffs Harbour, NSW 2450, Australia; [email protected] 3 Sci-eye, P.O. Box 4202, Goonellabah, NSW 2480, Australia; [email protected] (A.P.C.); [email protected] (A.J.W.) 4 SMART Infrastructure Facility, University of Wollongong, Wollongong, NSW 2522, Australia; [email protected] 5 Department of Biological Sciences, Florida Atlantic University, Boca Raton, FL 33431, USA; [email protected] 6 Marine Futures Lab, School of Biological Sciences, University of Western Australia, Crawley, WA 6009, Australia; [email protected] 7 UMS 3514 Plateforme Marine Stella Mare, Université de Corse Pasquale Paoli, 20620 Biguglia, France; [email protected] 8 Department of Physics and Astronomy, Faculty of Science and Engineering, Macquarie University, Sydney, NSW 2109, Australia; [email protected] 9 Sydney Institute for Astronomy (SIfA), School of Physics, The University of Sydney, Sydney, NSW 2006, Australia 10 Massachusetts Division of Marine Fisheries, 836 South Rodney
    [Show full text]
  • Response of Wave-Dominated and Mixed-Energy Barriers to Storms
    RESPONSE OF WAVE-DOMINATED AND MIXED-ENERGY BARRIERS TO STORMS Gerd Masselink1 & Sytze van Heteren2 1School of Marine Science and Engineering, Plymouth University, Plymouth, UK 2Geological Survey of the Netherlands, Utrecht, The Netherlands Marine Geology, 352, 321-347, doi: 10.1016/j.margeo.2013.11.004 http://www.sciencedirect.com/science/article/pii/S0025322713002442 NOTICE: this is the author’s version of a work that was accepted for publication in Marine Geology. Changes resulting from the publishing process, such as peer review, editing, corrections, structural formatting, and other quality control mechanisms may not be reflected in this document. Changes may have been made to this work since it was submitted for publication. A definitive version was subsequently published in Marine Geology, [VOL 352, (15th Nov 2013 )] DOI 10.1016/j.margeo.2013.11.004 Response of wave-dominated and mixed-energy barriers to storms (11,700 words; 22 figures; 1 table) Abstract (500 words) 1. Introduction (1200; 2 figures) 2. Long-term influences: sea-level change and storminess (1000; 1 figure) 3. Factors influencing the impact of individual storms (1200) 4. Hydrodynamic processes during storms (2100; 6 figures, 1 table) 4.1 Weather and storm surge (300; 1 figure) 4.2 Surf zone waves and currents (900; 4 figures, 1 table) 4.3 Sediment fluxes and budgets (900; 1 figure) 5. Barrier response to storm-generated hydrodynamic processes (3600; 4 figures) 5.1 Storm-Impact Scale model and the role of freeboard (700; 1 figure) 5.2 Swash regime (900; 2 figures) 5.3 Collision regime (600; 1 figure) 5.4 Overwash regime (600) 5.5 Inundation regime (600) 5.6 Long-term response (200) 6.
    [Show full text]