|Scientific Name:||Hippocampus histrix|
|Species Authority:||Kaup, 1856|
|Red List Category & Criteria:||Vulnerable A2cd+4cd ver 3.1|
|Reviewer/s:||O’Donnell, K. & Foster, S.|
Hippocampus histrix was previously listed as Data Deficient but new information from trade surveys, and international trade data made available since the listing of seahorses on Appendix II of CITES in 2004, has allowed us to suspect a population decline of at least 30% over the last 10–15 years and that these declines are suspected to continue into the future. There are also concerns about habitat destruction and capture of seahorses as bycatch throughout the range of H. histrix. For these reasons, this species is listed as Vulnerable under criterion A.
Using data from the CITES Trade Database, it was found that this species is widely traded in both the live and dry trade throughout it's range and that trade is continuing (Evanson et al. 2011, UNEP-WCMC 2012a). Historical trade surveys report trade in this species from the mid 1990's in various parts of its global range (McPherson and Vincent 2004, Meeuwig et al. 2006, Perry et al. 2010) and even at this stage, interviews with fishers and traders reported declines in availability of seahorses in some countries (McPherson and Vincent 2004, Perry et al. 2010). Together this information demonstrates that there has been substantial pressure on wild populations for well over 10 years and that these pressures are continuing.
|Range Description:||Hippocampus histrix is relatively rare but widespread throughout the Indo-Pacific (Lourie et al. 2004).|
Native:China; French Polynesia; Indonesia; Japan; Malaysia; Mauritius; Micronesia, Federated States of ; New Caledonia; Papua New Guinea; Philippines; Réunion; Samoa; South Africa; Tanzania, United Republic of; Tonga; United States (Hawaiian Is.); Viet Nam
|FAO Marine Fishing Areas:||
Indian Ocean – eastern; Indian Ocean – western; Pacific – eastern central; Pacific – northwest; Pacific – western central
|Range Map:||Click here to open the map viewer and explore range.|
There is little information on population levels and trends for Hippocampus histrix but it can be suspected that population levels are decreasing due to exploitation for international trade, coupled with high levels of bycatch and habitat destruction of H. histrix's primary habitat, seagrasses.
In parts of its range fishers and traders have reported declines in the availability and/or size of seahorses. For example, in 1998 and 1999 in Malaysia and Thailand, surveys of both fishers and traders reported declines in the availability of seahorses including H. histrix (Perry et al. 2010). There are also reports of general seahorse declines in the Philippines (O'Donnel et al. 2010). In East Africa, surveys of fishers and traders in 2000 documented declines in seahorse availability and size, which included H. histrix (McPherson and Vincent 2004). Currently, trade in this species is extensive with annual reported volumes exceeding 200 thousand individuals annually between 2004 and 2010 from a number of countries throughout this species' range (Evanson et al. 2011, UNEP-WCMC 2012a). Trade in seahorses, is expected to continue into the future as the demands for traditional medicines increase due to their increasing popularity in both the developed and developing world (Robinson and Zhang 2011).
General seahorse population declines within H. histrix's range are suspected as a result of habitat degradation and declines in seagrasses (Marcus et al. 2007, Short et al. 2011), and mortality from intense trawling bycatch (Baum et al. 2003, Giles et al. 2006, Perry et al. 2010) - and indeed these threats are known to occur throughout this species' range (FAO 2001, Perry et al. 2010).
Since trade is reported for several different parts of this species' range and that the threats facing this species occur throughout its range, it is suspected that these declines are occurring globally for H. histrix. It is conservatively suspected that the rate of decline has been at least 30% for the past 10–15 years and that this decline is expected to continue into the future.
|Habitat and Ecology:||
Hippocampus histrix is often found at depths between six and 20 m (Lourie et al. 2004) but may also be found deeper than this (Kuiter 2000). This species is found on a variety of substrates including sponges, weedy rocky reefs, soft corals but mainly on seagrass beds (Lourie et al. 2004, Kuiter 2000).
All seahorse species have vital parental care, and many species studied to date have high site fidelity (Perante et al. 2002, Foster and Vincent 2004), highly structured social behaviour (Vincent and Sadler 1995), and relatively sparse distributions (Lourie et al. 1999) - all traits which make seahorses vulnerable to exploitation. There are however some traits, such as small body size, fast growth and high fecundity that may make seahorses more resilient to exploitation (Morgan 2007). However a specialised life-history coupled with a dependence on shallow habitats that are subject to extremely high fishing pressure, and the fact that seahorses do not move very much and are thus easily captured, means they are very vulnerable to over-exploitation. The importance of life history parameters in determining response to exploitation has been demonstrated for a number of species, including seahorses (Jennings et al. 1998, Foster and Vincent 2004).
The major threat to Hippocampus histrix is international trade for the aquarium and traditional medicine trades. To supply this trade, this species is caught in both targeted fisheries as well as bycatch in other non-selective fisheries, particularly shrimp trawls (McPherson and Vincent 2004, Meeuwig et al. 2006, Perry et al. 2010). H. histrix has been reported in international trade since the mid 1990's and even at this stage, interviews with fishers and traders reported declines in the availability of seahorses (McPherson and Vincent 2004, Perry et al. 2010).
Even without demand for trade, this species is known to be a bycatch in the tropical shrimp trawl fishery and shrimp trawling is known to occur throughout much of its range and cause substantial damage to this species' habitats (FAO 2001, Perry et al. 2010).
Indeed, this species' in-shore seagrass habitats are threatened throughout its range (Short et al. 2011). Major threats faced by seagrasses include; eutrophication, sedimentation, coastal construction, dredging and invasive species and these threats result in decline in and fragmentation of seagrass habitats (see Short et al. 2011 for an overview of threats facing seagrasses). It is reasonable to expect that all of these threats will continue into the future.
Seahorses life history and ecological traits may increase their susceptibility to these threats (see Habitats and Ecology).
All Hippocampus species are listed under Appendix II of the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES). This means that countries who are signatories to CITES are subject to regulations on the export of seahorses. Countries are required to provide permits for all exports of seahorses and are meant to provide evidence that these exports are not detrimental to wild populations. However a lack of basic information on distribution, habitat and abundance means many CITES Authorities cannot assess sustainability of their seahorse exploitation and meet their obligations to the Convention. The challenge is particularly large in that most seahorses entering trade are caught incidentally as bycatch and thus imposing export quotas would achieve next to nothing for wild populations.
CITES has recommended a minimum size limit of 10 cm height for all seahorse specimens in trade (CITES Decision 12.54). This limit represents a compromise between the best biological information available at the time of listing and perceived socioeconomic feasibility. But we urgently need information on wild populations to assess their conservation status and take conservation action, as well as refine management recommendations. For example, evidence on variation in the spatial and temporal abundance of seahorses would enable areas of high seahorse density to be identified, as the basis for considering area restrictions on non-selective fishing gear that obtains Hippocampus species as bycatch. An understanding of the technical and logistical feasibility of returning to the sea live seahorses taken as bycatch in various types of fishing gear would provide the basis for considering the feasibility of minimum size limits and/or other output controls. Establishing monitoring program of landings of seahorses at representative sites, taking into account different gear types and means of extraction and recording catch and effort metrics would allow us to assess population conservation status and develop management recommendations for various fishery types.
Hippocampus histrix has been listed as Data Deficient in the Vietnamese Red Data Book.
Evanson, M., Foster, S. J. & Vincent, A. C. J. 2011. Tracking the international trade of seahorses (Hippocampus species) - The importance of CITES. Fisheries Centre Research Reports 19(2). Fisheries Centre, University of British Columbia, Canada.
FAO. 2001. Tropical shrimp fisheries and their impact on living resources. Shrimp fisheries in Africa: Cameroon, Nigeria and the United Republic of Tanzania. FAO Fisheries Circular. No. 974. Food and Agriculture Organization of the United Nations, Rome.
Foster, S.J. and Vincent, A.C.J. 2004. Life history and ecology of seahorses: implications for conservation and management. Journal of Fish Biology 65: 1-61.
Indian Ministry of Environments and Forests. 2001. Amendments to Schedule I and Schedule III of the Wild Life (Protection) Act, 1972 (53 of 1972)..
IUCN. 2002. 2002 IUCN Red List of Threatened Species. www.iucnredlist.org. Downloaded on 8 October 2002.
IUCN. 2012. IUCN Red List of Threatened Species (ver. 2012.2). Available at: http://www.iucnredlist.org. (Accessed: 17 October 2012).
Jennings, S., Reynolds, J.D. and Mills, S.C. 1998. Life history correlates of responses to fisheries exploitation. Proceedings of the Royal Society of London Series B 265:333-339.
Kuiter, R.H. 2000a. Seahorses, Pipefishes and their Relatives. A Comprehensive Guide to Syngnathiformes. TMC Publishing, Chorleywood, UK.
Lourie, S.A., Foster, S.J., Cooper, E.W.T. and Vincent, A.C.J. 2004. A Guide to the Identification of Seahorses. Project Seahorse and TRAFFIC North America, University of British Columbia and World Wildlife Fund, Washington D.C.
Lourie, S.A., Vincent, A.C.J. and Hall, H.J. 1999. Seahorses: an identification guide to the world's species and their conservation. Project Seahorse, London, U.K.
McPherson, J. M. & Vincent, A.C.J. 2004. Assessing East African trade in seahorse species as a basis for conservation under international controls. Aquatic Conservation-Marine and Freshwater Ecosystems 14: 521-538.
Meeuwig, J.J., Hoang, D.H., Ky, T.S., Job, S.D. and Vincent, A.C.J. 2006. Quantifying non-target seahorse fisheries in central Vietnam. Fisheries Research 81: 149-157.
Morgan, S.K. 2007. THE ONTOGENETIC ECOLOGY AND CONSERVATION OF EXPLOITED TROPICAL SEAHORSES. Department of Biology, McGill University.
O'Donnell, K.P., Pajaro, M.G., and Vincent, A.C.J. 2010. How does the accuracy of fisher knowledge affect seahorse conservation status? Animal Conservation 13(6): 526-533.
Perante, N.C., Pajaro, M.G., Meeuwig, J.J. and Vincent, A.C.J. 2002. Biology of a seahorse species Hippocampus comes in the central Philippines. Accepted by Journal of Fish Biology. 2001.
Perry, A. L., Lunn, K. E. & Vincent, A. C. J. 2010. Fisheries, large-scale trade, and conservation of seahorses in Malaysia and Thailand. Aquatic conservation: marine and freshwater ecosystems 20: 464-475.
Philippine Department of Agriculture. 1998. The Philippine Fisheries Code of 1998: Republic Act No. 8550.
Robinson, M.M. and Zhang, X. 2011. The world medicine situation 2011 (Traditional medicine: global situation, issues, and challenges). World Health Organisation (WHO), Geneva.
UNEP-WCMC. 2012a. CITES trade statistics derived from the CITES Trade Database. UNEP World Conservation Monitoring Centre, Cambridge, UK.
UNEP-WCMC. 2012b. Review of Significant Trade: Species selected by the CITES Animals Committee following CoP15.
Vincent, A.C.J. 1996. The International Trade in Seahorses. TRAFFIC International, Cambridge, UK.
Vincent, A.C.J. and Sadler, L.M. 1995. Faithful pair bonds in wild seahorses, Hippocampus whitei. Animal Behaviour 50: 1557-1569.
Vincent, A.C.J., Evans, K.L., and Marsden, A.D. 2005. Home range behaviour of the monogamous Australian seahorse, Hippocampus whitei. Environmental Biology of Fishes 72: 1–12.
Vincent, A. C. J., Foster, S. J. & Koldewey, H. J. 2011a. Conservation and management of seahorses and other Syngnathidae. Journal of fish biology 78: 1681-1724.
Vincent, A. C. J., Giles, B. G., Czembor, C. A. & Foster, S. J. 2011b. Trade in seahorses and other syngnathids in non-Asian countries (1998-2001). Fisheries Centre Research Reports 19(1). Fisheries Centre, University of British Columbia [ISSN 1198-6727].
|Citation:||Wiswedel, S. 2012. Hippocampus histrix. In: IUCN 2013. IUCN Red List of Threatened Species. Version 2013.2. <www.iucnredlist.org>. Downloaded on 13 December 2013.|
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