First published online January 25, 2005
Journal of Experimental Biology 208, 505-513 (2005)
Published by The Company of Biologists 2005
doi: 10.1242/jeb.01415
Behavioural response to the bioavailability of inorganic mercury in the hydrothermal mussel Bathymodiolus azoricus
Enikõ Kádár*,
Valentina Costa,
Ricardo S. Santos and
Humberto Lopes
IMAR Centre of the University of Azores, Department of Oceanography
and Fisheries, 9900 Horta, Portugal

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Fig. 1. Schematic diagram of the apparatus used for monitoring shell gaping of the
vent mussel B. azoricus consisting of (a) a pair of electric sensors
attached to the edge of the shell that permits free movements of the animal;
(b) experimental closed-system aquarium housing 20 animals; (c) signal
amplifier and (d) computer interface that uses the signal analysis system
Signalview (Real Time Devices USA, Inc., 1994) to produce the output (e), the
`mussel actograph'.
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Fig. 2. Total Hg concentration in the soft tissues (gill, digestive gland, mantle
and foot) and byssus threads of the vent mussel B. azoricus kept in
seawater for 3 weeks (Control), followed by daily exposure to 20 µg
l-1 inorganic Hg for 3 weeks (Exposure) followed by transfer to
Hg-free seawater for an additional 3 weeks (Recovery). Vertical bars represent
mean concentrations ± S.E.M. (N=15) in animals
dissected at the end of each week of Control, Exposure and Recovery.
Statistical differences between tissue levels at different experimental times
was tested by one-way analysis of variance. Columns with the same letters are
not significantly different according to a S-N-K multiple range test
(P<0.05).
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Fig. 3. Total Hg concentration in the pooled pseudofaeces of 20 mussels that were
kept in seawater for 3 weeks (Control), then exposed daily to 20 µg
l-1 inorganic Hg for 3 weeks (Exposure), followed by transfer to
Hg-free seawater for a further 3 weeks (Recovery). Vertical bars represent
means ± S.E.M. (N=3).
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Fig. 4. Effect of inorganic Hg on (A) the duration and (B) frequency of shell
gaping activity of the vent mussel B. azoricus during 3 weeks in
seawater (Control) followed by 3 weeks of daily exposure to 20 µg
g-1 inorganic Hg, and an additional 3 weeks in Hg-free seawater
(Recovery). Vertical bars represent means of replicate mussels ±
S.E.M. (N=3). Statistical significance of Hg on shell
gaping was tested by one-way analysis of variance, and post-hoc tests
were performed to detect differences at different experimental moments,
indicated by asterisks (**P=0.001 and
***P<0.001). See
Table 1 for further
details.
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© The Company of Biologists Ltd 2005