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Abstract(s)
The salema, Sarpa salpa (Linnaeus, 1758), is a sparid with a
distribution that includes the eastern Atlantic coast from the
Bay of Biscay to South Africa, as well as the Azores, Madeira,
Canary and Cape Verde archipelagos. It is also found in
groups in the Mediterranean Sea and the Indian Ocean from
South Africa to Mozambique, living on sandy and seagrass
bottoms ranging from 0 to 70 m depth (Bauchot and Hureau,
1986). The species is a protandrous hermaphrodite where,
according to Criscoli et al. (2006), sex change occurs between
24 and 31 cm total length (3–7 years old).
While the economic value of S. salpa in fisheries is relatively
limited, its ecological importance is well recognized, with
several studies on its biology and interactions on seagrass
meadows (e.g. Verlaque, 1990; Criscoli et al., 2006). As an
herbivore Sarpa salpa has a strong impact with seagrass
meadows, being responsible for much of the herbivory
(Verlaque, 1990; Cebria´n et al., 1996; Prado et al., 2008),
and representing a considerable part of the ichthyofauna in
these habitats (Francour, 1997, 2000).
Studies on S. salpa diel activity patterns, home range and
habitat utilization in the Mediterranean Sea were undertaken
by Jadot et al. (2002, 2006). These studies have revealed two
behaviours, with some fish being highly sedentary while others
use larger areas; great variation in mobility was found, with
some fish showing both behaviours. The core areas (95%)
range between 1600 and 279 000m2
, with some fish presenting
diel movement patterns between day and night areas as well as
homing abilities.
The Ria Formosa, in the southern part of Portugal, is a
shallow coastal lagoon with large meadows of seagrasses
(Zostera noltii, Zostera marina and Cymodocea nodosa) where
the influence of S. salpa on these communities is still unknown.
Previous studies on the ichthyofauna of the Ria Formosa
coastal lagoon focused largely on temporal and spatial changes
in species composition (Monteiro et al., 1990; Ribeiro et al.,
2006, 2008). Up to the present, the acoustic telemetry studies
carried out in the Ria Formosa focused on the movements and
home range of Sparus aurata (Abecasis and Erzini, 2008) and
Diplodus spp. (Abecasis et al., 2009).
A preceding tag-recapture study of juveniles of S. salpa
(between 8.2 and 16.7 cm total length) provided limited
information, with only a few recaptures (Abecasis, 2007).
The present study was carried out to determine the movement
patterns of S. salpa inside a coastal lagoon (Ria Formosa,
south Portugal) in order to provide basic information on their
home range and site fidelity.
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Blackwell Publishing
