
Laboratory Evaluation of the Effects of Turbine Noise on Fish MICHELE HALVORSEN TOM CARLSON ANDREA COPPING Pacific Northwest National Laboratory Marine Sciences Laboratory, Sequim and Seattle, WA Recent Developments in Research on the Environmental Effects of MHK Technologies Washington DC April 9th 2013 April 17, 2013 Department of Energy 1 Components of Underwater Noise Sound energy can cause damage based on: Frequency Intensity Spectrum Two components of any sound wave: Pressure Particle motion Near field (pressure & particle motion) Far field (mostly pressure, but some motion) All fish can acoustically detect particle motion Some fish are acoustically sensitive to pressure . Marine energy development raises concerns about noise impacts on fish: . Typical assessments to determine harm include: . Auditory – hearing shift . Barotrauma – tissue/organ damage April 17, 2013 DOE Underwater Noise Effects - Auditory Impulse/Pile Tidal Chk Salmon Black Bass Dab 160 150 140 130 Auditory 120 Changes in SPL 1µPa) (dBre 110 hearing threshold 100 Masking 90 80 100 200 300 400 500 600 700 800 Frequency (Hz) Salmon: Halvorsen et.al., 2009; Bass: Holt et.al., 2010; Dab: Chapman & Sand 1973; AprilKarl 17, von 2013 Frisch - ear 3 Underwater Noise Effects - Barotrauma Barotrauma is tissue injury caused by rapid pressure changes Impulsive Sounds Intermittent and Continuous Sounds Pile driving Low- and mid-frequency sonar Seismic exploration Shipping Explosions Wave energy converters Tidal turbines Wind farms April 17, 2013 DOE 4 Underwater Noise Effects - Barotrauma Swim bladder Contracts and expands Rupture Damages surrounding tissues Dissolved blood gasses come out of solution Bubbles form in blood and tissues Damages tissues, vessels, organs Equilibration state of animal is important Neutrally buoyant fish Tissue-gas equilibration with surrounding water Physiological state of fish at exposure is critical (mimic state of wild fish) April 17, 2013 DOE 5 Testing Methods Salmon and Bass Detailed External Detailed Internal Barotrauma Necropsy Exam Exam Tidal Turbine Noise Exposure 24 hours Auditory Evoked Changes in threshold Hearing Test Potential - AEP sensitivity Salmon only April 17, 2013 6 Noise from OpenHydro tidal turbine Turbine spectrogram Measured at EMEC Laboratory experiments Continuous noise exposure Physiological response of fish to sound exposure April 17, 2013 7 Tidal Turbine Noise and Fish Audiograms April 17, 2013 8 Tidal Turbine- Hearing Tests Respiration reservoir Hydrophone Hearing test Respiration tube holder Fish holder Electrode wires AEP tank BioAmps April 17, 2013 DOE 9 Tidal Turbine - Auditory Evoked Potentials Brain activity - synchronized to the sound wave Louder level Softer level Outcome for juvenile salmon: Synchronized Brain activity disappeared = no detection NSS difference between test and control exposures @ 158- 162dB April 17, 2013 DOE 10 Barotrauma Exposure and Effects Response Model Barotrauma Used panel of 72 injuries to assess biological effects Purpose “Quantify a qualitative assessment” Focused on physiological ‘meaning’ of observed injuries Fish Index Trauma - FIT List of 72 injuries Physiological Rank 3 Injury classes Response Weighted Index (RWI) Weight RWI = ∑ (W x Ti) Mortal Injury Wt Moderate Injury Wt Mild Injury Wt Dead within 1 hr 5 Hemorrhage: intestine 3 Hematoma : vent 1 Hemorrhage: heart 5 Hemorrhage: wall capillaries 3 Hematoma: dorsal fin 1 11 April 17, 2013 DOE Fish Physiology Groups Physostomous Physoclistous 12 Connection between gut and Closed swim bladder swim bladder Small organ for gas exchange to Gulp or burp air fill or empty swim bladder Need access to air to increase Need time – several hours to swim bladder volume change swim bladder volume SALMON BASS April 17, 2013 DOE Results - Barotrauma Salmon Largemouth Bass 90.0 CONTROL BASS EXPOSED BASS 90.0 CONTROL SALMON EXPOSED SALMON 80.0 80.0 70.0 70.0 60.0 60.0 50.0 50.0 40.0 40.0 30.0 30.0 20.0 20.0 10.0 10.0 Proportion of injury occurance occurance injury (unweighted) of Proportion Proportion of injury occurance occurance injury (unweighted) of Proportion 0.0 0.0 April 17, 2013 DOE 13 Explanation of Barotrauma Results Salmon and bass showed low levels of hemorrhages in their tissues, considered to be recoverable Both species have deflated their swimbladders, probably due to combination of: Stress Active management Bass actively empty their swim bladder over time Salmon quickly empty swim bladder with a burp, then refill with gulps of air April 17, 2013 14 Effects of Tidal Turbine Sound on Fish “Worst case” levels of noise for one turbine (OH) Tested juvenile salmon and largemouth bass (surrogate for rockfish) Noise equivalent to placing fish next to turbine, no avoidance Exposure for up to 24 hours (continuous, longer than tidal cycle) Barotrauma appears to be minor, recoverable as fish moves away Hearing shift for salmon not significant BUT need more info on: Hearing shift in other fish groups Effects in barotrauma and hearing shift on elasmobranchs Sound from other turbine types Effects of arrays of turbines (additive, multiplicative) at commercial buildout April 17, 2013 15 Thank you! We would like to acknowledge the generous support of the US Department of Energy Wind & Water Power Technologies Office, our project partners, and the cooperation of MHK technology and project developers. Michele B Halvorsen [email protected] 360-681-3697 Thomas J Carlson [email protected] 503-417-7562 Andrea E. Copping [email protected] 206-528-3049 .
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