First published online August 31, 2004
Journal of Experimental Biology 207, 3591-3602 (2004)
Published by The Company of Biologists 2004
doi: 10.1242/jeb.01188
Acoustical stress and hearing sensitivity in fishes: does the linear threshold shift hypothesis hold water?
Michael E. Smith1,*,
Andrew S. Kane2 and
Arthur N. Popper1,3
1 Department of Biology and Center for Comparative and Evolutionary Biology
of Hearing, University of Maryland, College Park, MD 20742, USA
2 Aquatic Pathobiology Program, Department of Veterinary Medicine,
University of Maryland, College Park, MD 20742, USA
3 Neuroscience and Cognitive Science Program, University of Maryland,
College Park, MD 20742, USA

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Fig. 1. The power spectra level of the 170 dB re 1 µPa white noise used for
noise exposure experiments (from Smith et
al., 2004 ). The top curve shows the spectrum as recorded directly
from the MiniDisc player. The bottom curve shows the spectrum as recorded by a
hydrophone placed centrally within the noise exposure bucket. The spectrum
measured within the noise exposure aquarium is similar to that of the bucket,
so it is omitted for clarity.
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Fig. 2. Mean (± S.E.M.) auditory thresholds
of control (110 dB re 1 µPa) and noise-exposed (130160 dB re 1
µPa) goldfish after 24 h of white noise exposure.
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Fig. 3. Temporary threshold shift (TTS) as a function of absolute sound pressure
level (SPL) of the exposure noise. Data points represent mean (±
S.E.M.) TTS across five frequencies
(4002000 Hz), with N=6 fish for each frequency. The line
represents the linear regression equation for the data shown.
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Fig. 4. Temporary threshold shift (TTS) as a function of sound pressure differences
(SPD) between the noise exposure sound pressure level (SPL) and goldfish
baseline auditory threshold SPL. This relationship is shown at (A) different
frequencies tested and (B) different noise SPL used. Colored lines in A
represent separate linear regressions for each frequency tested, while in B
they represent separate linear regressions for each of the four SPLs (130,
140, 160 or 170 dB re1 µPa) at all frequencies tested. Each data point is
the mean TTS for a particular frequency (N=6 fish). The same data
points are plotted in A and B, but the individual data points are not shown in
A for clarity.
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Fig. 5. Mean (± S.E.M.) temporary threshold
shift (TTS) for all sound pressure levels (SPL) tested (130, 140, 160, 170 dB
re 1 µPa) as a function of frequency (blue circles). The baseline goldfish
audiogram (black circles) is presented for comparison to show the relationship
between baseline thresholds and TTS.
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Fig. 6. Mean (± S.E.M.) auditory thresholds
of control and noise-exposed (A) tilapia and (B) goldfish after 7 and 21 or 28
days noise exposure. N=56.
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Fig. 7. Temporary threshold shift (TTS) as a function of noise sound pressure
differences (SPD) between the noise exposure sound pressure level (SPL) and
baseline hearing threshold SPL of five species of teleost. The line shows the
linear regression relationship for all the species
(TTS=0.23x2.44, r2=0.62).
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Fig. 8. Temporary threshold shift (TTS) as a function of noise sound pressure
differences (SPD) between the noise exposure sound pressure level (SPL) and
baseline hearing threshold SPL of birds, fish (hearing specialists only) and
mammals. Lines represent significant linear regression relationships
(TTSbirds=0.55x8.64, r2=0.36;
TTSfish=0.24x3.17, r2=0.54;
TTSmamm=0.55x57.64,
r2=0.81).
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© The Company of Biologists Ltd 2004