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Acoustic Effects on Fish
and Data Gaps
CSA Ocean Sciences Inc.
Michele B. Halvorsen Ph.D.
CEFAS/TNO EU Workshop 10 April 2014
• Energy development in marine environments
• Installation
• Decommissioning
• Operation
• Seismic
• Pile driving
• Blasting
• Naval sonars
• Tidal and Wave Turbine
• Wind Farms
• Drilling
• Subsea maintenance stations
• Shipping
• commercial
• recreational
• Transportation
• Ice breakers
• Dredging
• Bridges
• Trains
• Vehicles
Anthropogenic Underwater Noise Sources
Halvorsen 2014 CEFAS Workshop
Underwater Noise Components
• Sound energy can cause damage
• Frequency
• Intensity
• Two components of any sound wave
• Pressure
• Particle motion
• Near field (pressure & particle motion)
• Far field (mostly pressure, but some motion)
Halvorsen 2014 CEFAS Workshop
Concern for aquatic animals – Long Term
Commercial and Responsible Environmental Stewardship
• Death
• Auditory Temporary Threshold Shifts (TTS)
• Barotrauma (tissue damage)
• Behavioral Responses
• Auditory Masking
• Stress induced changes
• Behavioral
• Hormones
• Metabolism
• Cognition
• Sleep
• Immunity
• Reproduction
• Feeding
Underwater Noise Effects
Fitness
Halvorsen 2014 CEFAS Workshop
TTS
Barotrauma
Death
Halvorsen 2014 CEFAS Workshop
Source
Physiological Stress - Fitness
Physiological Stress - Fitness
Distance
Masking
Behavior (Acoustic - Context)
Lab Exposure and Assessment
Fis
h l
oa
din
g
Ex
po
sure
• Exposed fish to impulsive sounds
• SELcum 219 dB; 2000 and 1000 strikes
• Barotrauma injury assessments of neutrally buoyant fish
Halvorsen 2014 CEFAS Workshop
Fish Morphologies
Physostomous
Physoclistous ▫ Connection between gut
and swim bladder
▫ Gulp air or expel air
▫ Need air source
Closed swim bladder
Rete organ fills swim bladder
Needs time- several hours
Physoclistous
Halvorsen 2014 CEFAS Workshop
Lacking swim bladder
80
90
100
110
120
130
140
150
160
100 200 300 400 500 600 700 800
SP
L (
dB
re
1µ
Pa
)
Frequency (Hz)
Impulse/Pile Tidal Chk Salmon Black Bass Dab
Underwater Noise Effects - Auditory
Auditory
• Masking
• Hair cell damage
• TTS
Salmon: Halvorsen et.al., 2009; Bass: Holt et.al., 2010; Dab: Chapman & Sand 1973; Karl von Frisch- ear
Halvorsen 2014 CEFAS Workshop
Halvorsen 2014 CEFAS Workshop Casper BM, et al (2013). Effects of exposure to pile driving sounds on fish inner ear tissues. Comp Bioch and Phys A,
Control SELcum 216 dB strikes
Sensory Epithelium
• Defined threshold for trauma
• Barotrauma and Hair cell damage
• Created a single metric for tissue response
• Generated a model of responses
• Developed a tool to help define criteria
• Protect fish from impulsive sounds
Objectives
Halvorsen 2014 CEFAS Workshop
Summary of Sound Exposure Studies
• Barotrauma occurs before damage to hair cells (TTS)
• Physoclistous fish are more sensitive to sound (barotrauma) than physostomous
• Physoclistous fish deflated their swim bladder after 24 hours of noise exposure (Stress)
• Masking is a big issue and how that influences behavior
Halvorsen 2014 CEFAS Workshop
Key Points & Data Gaps
• Food webs all marine animals are connected
• Baseline data must be collected now
• Otherwise there is nothing to compare to later
• Behavior
• Masking
• Stress
• Long term elevated background noise levels
• Quieting methods
• Modeling sound budgets (now and in future)
Halvorsen 2014 CEFAS Workshop
• Needs/ Gaps
• Effects of depth on fish response (depth might be protective for barotrauma not hearing)
• Extrapolation of biological responses to other signals
• Testing various size classes within a species
• Different groups: Physoclistous, physostomous, no swim bladder
• Understand process of injury accrual (do silent breaks = “restart” for accumulation?)
• Exploration of assays to detect the presence of specific proteins (biomarkers) in blood
• Appropriate metric or group of metrics
Injury and Effects on Fish Physiology
Halvorsen 2014 CEFAS Workshop
Michele B Halvorsen CSA Ocean Sciences [email protected] 772-219-3027
Team Members Tom Carlson (PNNL) Art Popper (UMD) Brandon Casper (UMD) Christa Woodley (PNNL)