First published online September 9, 2005
Journal of Experimental Biology 208, 3533-3542 (2005)
Published by The Company of Biologists 2005
doi: 10.1242/jeb.01809
Are hearing sensitivities of freshwater fish adapted to the ambient noise in their habitats?
Sonja Amoser* and
Friedrich Ladich
University of Vienna, Department of Neurobiology and Behavior,
Althanstrasse 14, 1090 Vienna, Austria

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Fig. 1. Sound power spectra of the different ambient noise types recorded in the
four habitats and used as masking noise. DR, Danube river; TS, Triesting
stream; BW, backwater; LN, Lake Neusiedl. Note the linear frequency axis
scaling in this figure and the logarithmic scaling in Figs
2 and
4.
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Fig. 2. Mean hearing thresholds of Cyprinus carpio (solid lines) under
laboratory conditions (baseline) and in the presence of the different ambient
noise types. Broken lines show the cepstrum-smoothed sound power spectra of
the corresponding noise types (Fig.
1 shows the absolute amplitude spectra). DR, Danube river; TS,
Triesting stream; BW, backwater; LN, Lake Neusiedl.
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Fig. 3. Differences in hearing thresholds between the baseline audiogram of C.
carpio and the masked audiograms. Values are means ±
S.E.M. (N=6). Colours indicate the
differences for the respective habitats according to
Fig. 1. Blue, Danube river;
red, Triesting stream; green, backwater; orange, Lake Neusiedl.
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Fig. 4. Mean hearing thresholds of Perca fluviatilis (solid lines) under
laboratory conditions (baseline) and in the presence of the different ambient
noise types. Broken lines show the cepstrum-smoothed sound power spectra of
the corresponding habitat noise (Fig.
1 shows the absolute amplitude spectra). DR, Danube river; TS,
Triesting stream; BW, backwater; LN, Lake Neusiedl.
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Fig. 5. Differences hearing thresholds between the baseline audiogram of P.
fluviatilis and the masked audiograms. Values are means ±
S.E.M. (N=6). Colours indicate the
differences for the respective habitats according to
Fig. 4. Blue, Danube river;
red, Triesting stream; green, backwater; orange, Lake Neusiedl.
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Fig. 6. Threshold-to-noise ratios for masked thresholds of (A) C. carpio
(T/N-ratio = signal frequencyx0.0093+9.14, r=0.789,
P<0.001) and (B) P. fluviatilis (T/N-ratio = signal
frequency x0.0214+20.128, r=0.456, P<0.001).
Colours indicate the T/N ratios for the respective habitats according to
Fig. 1.
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© The Company of Biologists Ltd 2005