2012. Review of Significant Trade - Cites
2012. Review of Significant Trade - Cites
2012. Review of Significant Trade - Cites
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Mantella aurantiaca<br />
Taxonomic note: Up until just over a decade ago, species in the genus Mantella were<br />
distinguished largely subjectively on the basis <strong>of</strong> phenotypic variation, with different<br />
authors recognizing different numbers <strong>of</strong> species (Schaefer et al., 2002). M. aurantiaca is<br />
phenotypically and genetically distinct (e.g. Vences et al., 1999; Schaefer et al., 2002),<br />
although M. milotympanum is closely related to M. aurantiaca and was not described as a<br />
distinct species until 1996 (Randrianavelona et al., 2010b). Vences and Raxworthy (2008)<br />
reported that “The taxonomy <strong>of</strong> this group is uncertain but the definition <strong>of</strong><br />
Mantella aurantiaca is clear and there seems to be little genetic subdivision within the<br />
species”.<br />
C. Country review<br />
MADAGASCAR<br />
Distribution in range State: Mantella aurantiaca is known to occur only in the humid forests<br />
within the Moramanga District in eastern Madagascar (Randrianavelona et al., 2010a), where<br />
its distribution is highly localised in three distinct clusters <strong>of</strong> sites (Figure 1). Surveys by<br />
Bora et al. (2008) and Randrianavelona et al. (2010a) reported one cluster <strong>of</strong> 21 sites in the<br />
Andranomena-Mangabe forest in the municipalities <strong>of</strong> Ambohibary, Beparasy and<br />
Vodiriana to the south-west <strong>of</strong> Moramanga. Another cluster <strong>of</strong> sites was recorded in the<br />
Torotor<strong>of</strong>otsy wetlands in the municipality <strong>of</strong> Andasibe (five sites) and the surrounding<br />
forests in Analamay and Ambatovy in the municipality <strong>of</strong> Ambohibary (13 sites) to the<br />
north-east <strong>of</strong> Moramanga (Bora et al., 2008; Randrianavelona et al., 2010a). Bora et al. (2008)<br />
also recorded the species at two sites to the north-west <strong>of</strong> Moramanga in the Ambakoana<br />
region in the municipality <strong>of</strong> Amboasary. These data indicate a total extent <strong>of</strong> occurrence <strong>of</strong><br />
1189 km 2 and an area <strong>of</strong> occupancy <strong>of</strong> 112 km 2 , or 626 km 2 and 89 km 2 , respectively, if the<br />
outlying populations are not considered (Randrianavelona et al., 2010b). The discovery <strong>of</strong><br />
one population in the municipality <strong>of</strong> Vodiriana to the west <strong>of</strong> the Mangoro river, previously<br />
thought to be a barrier to dispersal (Randrianavelona, 2009), opens the possibility that the<br />
species may be present in new areas as yet unexplored by herpetologists<br />
(Randrianavelona et al., 2010b).<br />
The historical distribution <strong>of</strong> the species was much wider than its current distribution<br />
(Figure 1, Randrianavelona et al., 2010b). There have been various unconfirmed reports <strong>of</strong><br />
the species occurring in localities outside the three regions described above (e.g.<br />
Behra et al., 1995). Several <strong>of</strong> these records are thought to have been the result <strong>of</strong> confusion<br />
<strong>of</strong> M. aurantiaca with the related species M. milotympanum (Vences et al., 1999). Other records<br />
remain uncertain, including sites in Maromizaha, Ambavaniasy and the forest <strong>of</strong><br />
Vohidrazana (Behra et al., 1995), all <strong>of</strong> which were surveyed by Vieites et al. (2009) without<br />
success; and a site near Ankaratra, Ambatolampy (Behra et al., 1995), considered unlikely<br />
due to its altitude <strong>of</strong> over 1300m and the absence <strong>of</strong> humid forest<br />
(Randrianavelona et al., 2010b).<br />
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