2012. Review of Significant Trade - Cites
2012. Review of Significant Trade - Cites
2012. Review of Significant Trade - Cites
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Hippocampus spinosissimus<br />
MYANMAR<br />
Distribution in range State: The species reported to occur in the Andaman Sea in southern<br />
Myanmar, in the waters bordering Thailand (Lourie et al., 2005) and in Thandwe,<br />
Kyaukphyu, Launglone, Thayetchaung, Myeik and Kawthaung in the Bay <strong>of</strong> Bengal<br />
(A. M. Maung, in litt. to UNEP-WCMC, 2011).<br />
Population trends and status: The population <strong>of</strong> H. spinosissimus was considered to be small<br />
and discontinuous, based on how rarely the species was found as by-catch (A. M. Maung, in<br />
litt. to UNEP-WCMC, 2011).<br />
Threats: The species was reported not to be targeted directly by fisheries (A. M. Maung, in<br />
litt. to UNEP-WCMC, 2011).<br />
<strong>Trade</strong>: According to data in the CITES <strong>Trade</strong> Database, no trade from Myanmar was<br />
reported 2004-2010. Annual reports have not yet been received from Myanmar for 2008 or<br />
2009.<br />
Although the species was considered less desirable than other Hippocampus spp., its use was<br />
considered to be increasing, due to higher demand for traditional medicine (A. M. Maung, in<br />
litt. to UNEP-WCMC, 2011). The CITES Management Authority <strong>of</strong> Myanmar did not find<br />
any internal trade but noted that a survey <strong>of</strong> illegal trade is required (A. M. Maung, in litt. to<br />
UNEP-WCMC, 2011).<br />
Management: Legal protection <strong>of</strong> the species and regulation <strong>of</strong> harvest were reported to be<br />
absent (A. M. Maung, in litt. to UNEP-WCMC, 2011).<br />
PHILIPPINES<br />
Distribution in range State: The species was reported to occur in the Danajon Bank, <strong>of</strong>f the<br />
island <strong>of</strong> Bohol (Martin-Smith et al., 2004; Lourie et al., 2005), Dumaran (Palawan province),<br />
Cavite (Luzon Island), Cawangan [presumably Cawayan] (Masbate Island) and Cebu<br />
province (Bantayan Island, Panitugan Island) (Lourie et al., 2005).<br />
Population trends and status: The proportion <strong>of</strong> Hippocampus spp. catch accounted for by<br />
H. spinosissimus was considered to be relatively small in the central Philippines (pers. obs.<br />
Project Seahorse, 2003b). Declines <strong>of</strong> 50-95 per cent <strong>of</strong> Hippocampus spp. were reported by<br />
fishers in the Philippines between 1980 and 1997 (Pajaro, unpublished data, cited in Project<br />
Seahorse, 2003a) and targeted catches <strong>of</strong> H. spinosissimus showed declines <strong>of</strong> more than<br />
80 per cent within two months (Panes and Giles, 2004, cited in Morgan and Panes, 2008).<br />
A previously undocumented population <strong>of</strong> H. spinosissimus declined by more than 90 per<br />
cent between its discovery in May and surveys in October, due to exploitation by<br />
compressor divers (Martin-Smith et al., 2004).<br />
Threats: Hippocampus spp. was considered to be vulnerable due to trade for traditional<br />
medicine, curios and aquaria (Vincent, 1996), with annual Hippocampus spp. by-catch in the<br />
Philippines estimated at two to six million specimens (Pajaro, unpubl. data, cited in<br />
Vincent et al., 2011). Habitat destruction was considered a threat to Hippocampus spp.<br />
(Vincent, 1996)<br />
H. spinosissimus was reported to be threatened by destructive fishing methods, including<br />
through the use <strong>of</strong> dynamite and cyanide (Project Seahorse, 2003b). In the Philippines,<br />
H. spinosissimus was reported to be collected using SSBA (surface-supply breathing<br />
apparatus), enabling the collection <strong>of</strong> specimens at greater depths (Martin-Smith et al., 2004)<br />
and catches in 2003 were considered significant (S. Morgan & D. McCorry pers. comm., cited<br />
in Martin-Smith et al., 2004).<br />
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