Mapping Turbidity Currents Using Seismic Oceanography Title Page Abstract Introduction 1 2 E
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Turbidity Criterion for the Protection of Coral Reef and Hardbottom Communities
DRAFT Implementation of the Turbidity Criterion for the Protection of Coral Reef and Hardbottom Communities Division of Environmental Assessment and Restoration Florida Department of Environmental Protection October 2020 Contents Section 1. Introduction ................................................................................................................................. 1 1.1 Purpose of Document .......................................................................................................................... 1 1.2 Background Information ..................................................................................................................... 1 1.3 Proposed Criterion and Rule Language .............................................................................................. 2 1.4 Threatened and Endangered Species Considerations .......................................................................... 5 1.5 Outstanding Florida Waters (OFW) Considerations ........................................................................... 5 1.6 Natural Factors Influencing Background Turbidity Levels ................................................................ 7 Section 2. Implementation in Permitting ..................................................................................................... 8 2.1 Permitting Information ........................................................................................................................ 8 2.2 Establishing Baseline (Pre-project) Levels ........................................................................................ -
National Primary Drinking Water Regulations
National Primary Drinking Water Regulations Potential health effects MCL or TT1 Common sources of contaminant in Public Health Contaminant from long-term3 exposure (mg/L)2 drinking water Goal (mg/L)2 above the MCL Nervous system or blood Added to water during sewage/ Acrylamide TT4 problems; increased risk of cancer wastewater treatment zero Eye, liver, kidney, or spleen Runoff from herbicide used on row Alachlor 0.002 problems; anemia; increased risk crops zero of cancer Erosion of natural deposits of certain 15 picocuries Alpha/photon minerals that are radioactive and per Liter Increased risk of cancer emitters may emit a form of radiation known zero (pCi/L) as alpha radiation Discharge from petroleum refineries; Increase in blood cholesterol; Antimony 0.006 fire retardants; ceramics; electronics; decrease in blood sugar 0.006 solder Skin damage or problems with Erosion of natural deposits; runoff Arsenic 0.010 circulatory systems, and may have from orchards; runoff from glass & 0 increased risk of getting cancer electronics production wastes Asbestos 7 million Increased risk of developing Decay of asbestos cement in water (fibers >10 fibers per Liter benign intestinal polyps mains; erosion of natural deposits 7 MFL micrometers) (MFL) Cardiovascular system or Runoff from herbicide used on row Atrazine 0.003 reproductive problems crops 0.003 Discharge of drilling wastes; discharge Barium 2 Increase in blood pressure from metal refineries; erosion 2 of natural deposits Anemia; decrease in blood Discharge from factories; leaching Benzene -
Observations of Nearshore Infragravity Waves: Seaward and Shoreward Propagating Components A
JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 107, NO. C8, 3095, 10.1029/2001JC000970, 2002 Observations of nearshore infragravity waves: Seaward and shoreward propagating components A. Sheremet,1 R. T. Guza,2 S. Elgar,3 and T. H. C. Herbers4 Received 14 May 2001; revised 5 December 2001; accepted 20 December 2001; published 6 August 2002. [1] The variation of seaward and shoreward infragravity energy fluxes across the shoaling and surf zones of a gently sloping sandy beach is estimated from field observations and related to forcing by groups of sea and swell, dissipation, and shoreline reflection. Data from collocated pressure and velocity sensors deployed between 1 and 6 m water depth are combined, using the assumption of cross-shore propagation, to decompose the infragravity wave field into shoreward and seaward propagating components. Seaward of the surf zone, shoreward propagating infragravity waves are amplified by nonlinear interactions with groups of sea and swell, and the shoreward infragravity energy flux increases in the onshore direction. In the surf zone, nonlinear phase coupling between infragravity waves and groups of sea and swell decreases, as does the shoreward infragravity energy flux, consistent with the cessation of nonlinear forcing and the increased importance of infragravity wave dissipation. Seaward propagating infragravity waves are not phase coupled to incident wave groups, and their energy levels suggest strong infragravity wave reflection near the shoreline. The cross-shore variation of the seaward energy flux is weaker than that of the shoreward flux, resulting in cross-shore variation of the squared infragravity reflection coefficient (ratio of seaward to shoreward energy flux) between about 0.4 and 1.5. -
Infragravity Wave Energy Partitioning in the Surf Zone in Response to Wind-Sea and Swell Forcing
Journal of Marine Science and Engineering Article Infragravity Wave Energy Partitioning in the Surf Zone in Response to Wind-Sea and Swell Forcing Stephanie Contardo 1,*, Graham Symonds 2, Laura E. Segura 3, Ryan J. Lowe 4 and Jeff E. Hansen 2 1 CSIRO Oceans and Atmosphere, Crawley 6009, Australia 2 Faculty of Science, School of Earth Sciences, The University of Western Australia, Crawley 6009, Australia; [email protected] (G.S.); jeff[email protected] (J.E.H.) 3 Departamento de Física, Universidad Nacional, Heredia 3000, Costa Rica; [email protected] 4 Faculty of Engineering and Mathematical Sciences, Oceans Graduate School, The University of Western Australia, Crawley 6009, Australia; [email protected] * Correspondence: [email protected] Received: 18 September 2019; Accepted: 23 October 2019; Published: 28 October 2019 Abstract: An alongshore array of pressure sensors and a cross-shore array of current velocity and pressure sensors were deployed on a barred beach in southwestern Australia to estimate the relative response of edge waves and leaky waves to variable incident wind wave conditions. The strong sea 1 breeze cycle at the study site (wind speeds frequently > 10 m s− ) produced diurnal variations in the peak frequency of the incident waves, with wind sea conditions (periods 2 to 8 s) dominating during the peak of the sea breeze and swell (periods 8 to 20 s) dominating during times of low wind. We observed that edge wave modes and their frequency distribution varied with the frequency of the short-wave forcing (swell or wind-sea) and edge waves were more energetic than leaky waves for the duration of the 10-day experiment. -
Climate Change Report for Gulf of the Farallones and Cordell
Chapter 6 Responses in Marine Habitats Sea Level Rise: Intertidal organisms will respond to sea level rise by shifting their distributions to keep pace with rising sea level. It has been suggested that all but the slowest growing organisms will be able to keep pace with rising sea level (Harley et al. 2006) but few studies have thoroughly examined this phenomenon. As in soft sediment systems, the ability of intertidal organisms to migrate will depend on available upland habitat. If these communities are adjacent to steep coastal bluffs it is unclear if they will be able to colonize this habitat. Further, increased erosion and sedimentation may impede their ability to move. Waves: Greater wave activity (see 3.3.2 Waves) suggests that intertidal and subtidal organisms may experience greater physical forces. A number of studies indicate that the strength of organisms does not always scale with their size (Denny et al. 1985; Carrington 1990; Gaylord et al. 1994; Denny and Kitzes 2005; Gaylord et al. 2008), which can lead to selective removal of larger organisms, influencing size structure and species interactions that depend on size. However, the relationship between offshore significant wave height and hydrodynamic force is not simple. Although local wave height inside the surf zone is a good predictor of wave velocity and force (Gaylord 1999, 2000), the relationship between offshore Hs and intertidal force cannot be expressed via a simple linear relationship (Helmuth and Denny 2003). In many cases (89% of sites examined), elevated offshore wave activity increased force up to a point (Hs > 2-2.5 m), after which force did not increase with wave height. -
New York State Artificial Reef Plan and Generic Environmental Impact
TABLE OF CONTENTS EXECUTIVE SUMMARY ...................... vi 1. INTRODUCTION .......................1 2. MANAGEMENT ENVIRONMENT ..................4 2.1. HISTORICAL PERSPECTIVE. ..............4 2.2. LOCATION. .....................7 2.3. NATURAL RESOURCES. .................7 2.3.1 Physical Characteristics. ..........7 2.3.2 Living Resources. ............. 11 2.4. HUMAN RESOURCES. ................. 14 2.4.1 Fisheries. ................. 14 2.4.2 Archaeological Resources. ......... 17 2.4.3 Sand and Gravel Mining. .......... 18 2.4.4 Marine Disposal of Waste. ......... 18 2.4.5 Navigation. ................ 18 2.5. ARTIFICIAL REEF RESOURCES. ............ 20 3. GOALS AND OBJECTIVES .................. 26 3.1 GOALS ....................... 26 3.2 OBJECTIVES .................... 26 4. POLICY ......................... 28 4.1 PROGRAM ADMINISTRATION .............. 28 4.1.1 Permits. .................. 29 4.1.2 Materials Donations and Acquisitions. ... 31 4.1.3 Citizen Participation. ........... 33 4.1.4 Liability. ................. 35 4.1.5 Intra/Interagency Coordination. ...... 36 4.1.6 Program Costs and Funding. ......... 38 4.1.7 Research. ................. 40 4.2 DEVELOPMENT GUIDELINES .............. 44 4.2.1 Siting. .................. 44 4.2.2 Materials. ................. 55 4.2.3 Design. .................. 63 4.3 MANAGEMENT .................... 70 4.3.1 Monitoring. ................ 70 4.3.2 Maintenance. ................ 72 4.3.3 Reefs in the Exclusive Economic Zone. ... 74 4.3.4 Special Management Concerns. ........ 76 4.3.41 Estuarine reefs. ........... 76 4.3.42 Mitigation. ............. 77 4.3.43 Fish aggregating devices. ...... 80 i 4.3.44 User group conflicts. ........ 82 4.3.45 Illegal and destructive practices. .. 85 4.4 PLAN REVIEW .................... 88 5. ACTIONS ........................ 89 5.1 ADMINISTRATION .................. 89 5.2 RESEARCH ..................... 89 5.3 DEVELOPMENT .................... 91 5.4 MANAGEMENT .................... 96 6. ENVIRONMENTAL IMPACTS ................. 97 6.1 ECOSYSTEM IMPACTS. -
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WaveWave drivendriven sea-levelsea-level anomalyanomaly atat MidwayMidway AtollAtoll RonRon HoekeHoeke CSIROCSIRO SeaSea LevelLevel andand CoastsCoasts JeromeJerome AucanAucan LaboratoireLaboratoire d'Etudesd'Etudes enen GéophysiqueGéophysique etet OcéanographieOcéanographie SpatialeSpatiale (LEGOS),(LEGOS), IRDIRD MarkMark MerrifieldMerrifield SOESTSOEST –– UniversityUniversity ofof HawaiiHawaii Funding:Funding: ••NOAANOAA CRCPCRCP ••JIMARJIMAR –– UniversityUniversity ofof HawaiiHawaii ••AustralianAustralian InstituteInstitute ofof MarineMarine ScienceScience (AIMS)(AIMS) ••CSIROCSIRO SeaSea LevelLevel andand CoastsCoasts ((AusAID)AusAID) photo: Scott Smithers WaveWave set-upset-up atat PacificPacific atollsatolls andand islandsislands “..the power of the breaking waves is utilized to maintain a water level just inside the surf zone about 1.5 ft above sea level.” Munk and Sargent (1948) Adjustment of Bikini Atoll to waves, Transactions, Am. Geo. Union, 29(6), 855-860. Wave set-up may be “as much as 20% of the incident wave height.” Tait, R. J. (1972) Wave Set-Up on Coral Reefs, J. Geophys. Res., 77(12). WaveWave set-upset-up atat PacificPacific atollsatolls andand islandsislands Steep-sloped Continental Shelf: islands/atolls: Wave dissipation Wave dissipation close farther offshore to shore/reef edge Smaller waves Larger waves Larger storm surge Smaller storm surge Graber et al. (2006) Coastal forecasts and storm surge predictions for tropical cyclones: A timely partnership program, Oceanography, 19(1), 130–141. PacificPacific wavewave climateclimate Hoeke et al. (2011) J. Geophys. Res., 116(C4), C04018. WaveWave set-upset-up inundationinundation eventsevents Nov. 28, 1979 Pohnpei Majuro Dec. 8, 2008 Fiji T imes,May 21, 2011 Takuu Dec. 10, 2008 Caldwell,Vitousek, Aucan (2009), Frequency and Duration of Coinciding High Surf and Tides along the North Shore of Oahu, Hawaii, 1981-2007, J. -
Turbidity and Wave Energy Affect Community Composition and Trophic Interactions
TURBIDITY AND WAVE ENERGY AFFECT COMMUNITY COMPOSITION AND TROPHIC INTERACTIONS A Dissertation by JESSICA LUNT BS, University of West Florida, 2008 Submitted in Partial Fulfillment of the Requirements for the Degree of DOCTOR OF PHILOSOPHY in MARINE BIOLOGY Texas A&M University-Corpus Christi Corpus Christi, Texas August 2014 © Jessica Heath Lunt All Rights Reserved August 2014 TURBIDITY AND WAVE ENERGY AFFECT COMMUNITY COMPOSITION AND TROPHIC INTERACTIONS A Dissertation by JESSICA LUNT This dissertation meets the standards for scope and quality of Texas A&M University-Corpus Christi and is hereby approved. Delbert L. Smee, PhD Thomas C. Shirley, PhD Chair Committee Member Michael S. Wetz, PhD Anna R. Armitage, PhD Committee Member Committee Member Anita J. Reed, PhD Graduate Faculty Representative JoAnn Canales, PhD Dean, College of Graduate Studies August 2014 ABSTRACT Abiotic variables are well known community regulators and can strongly influence species distributions when they are outside of a species physiological tolerance limits. However, environmental variables within tolerance limits may also alter species distributions, morphology, predator-prey interactions, and influence the structure and function of communities. The purpose of this study was to determine how abiotic variables (notably turbidity) alter diversity, species distributions and abundances, predation rates on and species morphology. Texas Parks and Wildlife Department Fisheries Independent Survey Data from 1991- 2008 were used in addition to field surveys of St. Charles Bay to determine the effects of turbidity on fish and crab diversity and abundance. Feeding assays were conducted in the field using groups of 5 mud crabs and 10 juvenile oysters to assess feeding rates in high and low turbidity. -
Stratospheric Transport
Journal of the Meteorological Society of Japan, Vol. 80, No. 4B, pp. 793--809, 2002 793 Stratospheric Transport R. Alan PLUMB Department of Earth, Atmospheric and Planetary Sciences, Massachusetts Institute of Technology, Cambridge, MA 02139, USA (Manuscript received 3 July 2001, in revised form 15 February 2002) Abstract Improvements in our understanding of transport processes in the stratosphere have progressed hand in hand with advances in understanding of stratospheric dynamics and with accumulating remote and in situ observations of the distributions of, and relationships between, stratospheric tracers. It is conve- nient to regard the stratosphere as being separated into four regions: the summer hemisphere, the tropics, the wintertime midlatitude ‘‘surf zone’’, and the winter polar vortex. Stratospheric transport is dominated by mean diabatic advection (upwelling in the tropics, downwelling in the surf zone and the vortex) and, especially, by rapid isentropic stirring within the surf zone. These characteristics determine the global-scale distributions of tracers, and their mutual relationships. Despite our much-improved understanding of these processes, many chemical transport models still appear to exhibit significant shortcomings in simulating stratospheric transport, as is evidenced by their tendency to underestimate the age of stratospheric air. 1. Introduction have opposite large-scale gradients (HF has a stratospheric source and tropospheric sink, It has long been recognized that strato- CH a tropospheric source and stratospheric spheric trace gases with sufficiently weak 4 sink); nevertheless, the shapes of their iso- chemical sources and sinks have similar global pleths are very similar, with isopleths bulging distributions, in the sense that their isopleths upward in the tropics and poleward/downward (surfaces of constant mixing ratio) have similar slopes in the extratropics. -
Turbulence in the Swash and Surf Zones: a Review
Coastal Engineering 45 (2002) 129–147 www.elsevier.com/locate/coastaleng Turbulence in the swash and surf zones: a review Sandro Longo a,*, Marco Petti b,1, Inigo J. Losada c,2 aDepartment of Civil Engineering, University of Parma, Parco Area delle Scienze, 181/A, 43100 Parma, Italy bDipartimento di Georisorse e Territorio, Faculty of Engineering, University of Udine, Via del Cotonificio, 114, 33100 Udine, Italy cOcean and Coastal Research Group, Universidad de Cantabria, E.T.S.I.C.C. y P. Av. de los Castros s/n, 39005 Santander, Spain Abstract This paper reviews mainly conceptual models and experimental work, in the field and in the laboratory, dedicated during the last decades to studying turbulence of breaking waves and bores moving in very shallow water and in the swash zone. The phenomena associated with vorticity and turbulence structures measured are summarised, including the measurement techniques and the laboratory generation of breaking waves or of flow fields sharing several characteristics with breaking waves. The effect of air entrapment during breaking is discussed. The limits of the present knowledge, especially in modelling a two- or three-phase system, with air and sediment entrapped at high turbulence level, and perspectives of future research are discussed. D 2002 Elsevier Science B.V. All rights reserved. Keywords: Swash zone; Surf zone; Breaking waves; Turbulence; Length scales; Coastal hydrodynamics 1. Introduction short and long waves, currents, turbulence and vorti- ces may be present. Therefore, the hydrodynamics to The swash zone is defined as the part of the beach be found in the swash zone is largely determined by between the minimum and maximum water levels the boundary conditions imposed by the beach face during wave runup and rundown. -
Direct and Indirect Impacts of Turbidity and Diet on an African Cichlid Fish
Living in a haze: Direct and indirect impacts of turbidity and diet on an African cichlid fish Thesis Presented in Partial Fulfillment of the Requirements for the Degree Master of Science in the Graduate School of The Ohio State University By Tiffany Lynn Atkinson Graduate Program in Environment and Natural Resources The Ohio State University 2019 Thesis Committee Dr. Suzanne M. Gray, Advisor Dr. Lauren M. Pintor Dr. Roman P. Lanno Dr. Lauren J. Chapman Copyrighted by Tiffany Lynn Atkinson 2019 2 Abstract Worldwide, a major threat to aquatic systems is increased sediment runoff, which can lead to elevated levels of turbidity. In an increasingly variable world, the ability for animals to respond rapidly to environmental disturbance can be critical for survival. Chronic and acute turbidity exposure can have both indirect and direct effects on fish across large and small spatial scales. Indirect impacts include alteration of the sensory environment of fishes (disrupting communications) and shifts in prey availability; while direct impacts include damage to respiratory organs or eliciting physiological compensatory mechanisms that influence fitness- related traits associated with reproduction and survival. I used a combination of field and laboratory studies to examine the effects of elevated turbidity on an African cichlid fish (Pseudocrenilabrus multicolor victoriae). This sexually dimorphic species is widespread across the Nile River basin and is found across extreme environmental gradients (e.g. dissolved oxygen, turbidity). I investigated if within-population variation in diet and male nuptial coloration are associated with turbidity on a microgeographic spatial-scale. Diet was investigated because many cichlid fish depend on dietary carotenoids (red and yellow pigments) for their reproductive displays and other physiological mechanisms associated with health. -
Chapter 3—Relative Risks to the Great Barrier Reef from Degraded Water Quality
Scientific Consensus Statement 2013 – Chapter 3 ©The State of Queensland 2013. Published by the Reef Water Quality Protection Plan Secretariat, July 2013. Copyright protects this publication. Excerpts may be reproduced with acknowledgement to the State of Queensland. Image credits: TropWATER James Cook University, Tourism Queensland. This document was prepared by an independent panel of scientists with expertise in Great Barrier Reef water quality. This document does not represent government policy. 2 Relative risks to the Great Barrier Reef from degraded water quality Scientific Consensus Statement 2013 – Chapter 3 Table of Contents Executive summary .......................................................................................................................... 4 Introduction ..................................................................................................................................... 6 Synthesis process ............................................................................................................................. 7 Previous Consensus Statement findings ........................................................................................ 19 Current evidence on the relative risks of water quality pollutants to the Great Barrier Reef ...... 21 What is the current relative risk of priority pollutants to Great Barrier Reef marine systems? .............. 21 Where are the risks highest or the benefits of improved management greatest? .................................. 26 When are the risks