|Scientific Name:||Hippocampus breviceps|
|Species Authority:||Peters, 1869|
Hippocampus tuberculatus Castelnau, 1875
|Taxonomic Source(s):||Lourie, S.A., Pollom, R.A. and Foster, S.J. 2016. A global revision of the seahorses Hippocampus Rafinesque 1810 (Actinopterygii: Syngnathiformes): Taxonomy and biogeography with recommendations for future research. Zootaxa 4146(1): 1-66.|
|Taxonomic Notes:||Synonym = Hippocampus tuberculatus Castelnau, 1875.|
|Red List Category & Criteria:||Data Deficient ver 3.1|
|Assessor(s):||Morgan, S.K., Pogonoski, J.J., Pollard, D.A. & Paxton, J.R.|
|Reviewer(s):||Morgan, S.K. & Foster, S.J. (Syngnathid Red List Authority)|
At present, only rudimentary distribution data exist for H. breviceps and quantified abundance (density) comes from only one study in Port Philip Bay (Moreau and Vincent 2004). This area is noted for large H. breviceps populations and may not exhibit densities typical of most populations. Information regarding true occupancy (versus area of occurrence), and variation in densities within those areas of occupancy is lacking, as are data on population connectivity and basic life history parameters (in situ longevity, in situ fecundity, survivorship etc). No baseline data or monitoring programs presently exist against which to measure changes in population trends.
|Previously published Red List assessments:|
|Range Description:||H. breviceps is a temperate, southern Australian endemic seahorse, which is most common in the Port Philip Bay region of Victoria (Kuiter 1993). It is also known from Spencer Gulf and St. Vincent Gulf in South Australia, and Forsters Inlet southward to Port Arthur in eastern Tasmania (Lourie et al. 1999). It has also been recorded from Bass Strait (Last et al., 1983). Pogonoski et al. (2002) report that its occurrence in Western Australian waters is, at this stage, unclear. Lourie et al. (2004) note that some specimens from Western Australia have significantly longer, narrower snouts and may represent a separate species. This slender-snout form has only been seen in the northern portion of the species’ range, and is called H. tuberculatus (knobby seahorse) by Kuiter (1993). The range of H. breviceps falls within FAO fisheries area 57.|
Extent of occurrence includes Southern Australia, Victoria,Tasmania, and Western Australia. Area of occupancy includes documented populations in Port Philip Bay region of Victoria (Moreau and Vincent 2004), Spencer Gulf and St. Vincent Gulf in South Australia, Forsters Inlet southward to Port Arthur in eastern Tasmania (Lourie et al. 1999) and from the Bass Strait (Last et al. 1983).
Likely to inhabit the Blanche Harbour-Douglas Bank Aquatic Reserve (Marine Protected Area) in Spencer Gulf, Southern Australia (Pogonoski et al. 2002).
Native:Australia (South Australia, Tasmania, Victoria, Western Australia)
|FAO Marine Fishing Areas:|
Indian Ocean – eastern
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||No quantitative data exist on the estimated size of H. breviceps populations or subpopulations. Densities of 0.21 adults per square meter have been reported in the only studied population in Port Philip Bay. Research is required to determine the species’ genetic population structure and connectivity.|
|Current Population Trend:||Unknown|
|Habitat and Ecology:||Hippocampus breviceps occurs in sheltered coastal reefs in macroalgal beds (Sargassum spp.) (Moreau and Vincent 2004), within (Kendrick and Hyndes 2003) and at the edge of seagrass patches (Kuiter 2000). Individuals have also been found on floating macroalgae (Gomon et al. 1994), associated with rock reef and jetty habitats (Coleman 1980) and observed on sponge reefs at depths below 15 m (Kuiter 2000). Hippocampus breviceps are more normally found at depths of approximately 5 m, although may be difficult to see because of good camouflage (Edgar 1997). Specimens found in Sargassum usually have long fronds or appendages on the head and back. Hippocampus breviceps feeds close to the sand or rubble during the day and is carnivorous, targeting mysids (Kuiter 2000).
In Port Philip Bay animals occur in small to large aggregations (Kuiter 1993) with male;female sex ratios of 1:1 (Moreau and Vincent 2004). Group (2–5 individuals) occurrence coincides with particular seaweed areas that are the site of early morning social encounters (Moreau and Vincent 2004). Kuiter (2000) suggests that small groups congregate in safe places at night, often high in macroalgae to keep away from crabs on the substrate. Adults exhibit variable site fidelity, with 12 of 38 individuals remaining within a focal study area for five weeks of observation (Moreau and Vincent 2004). Females use significantly larger area than males (Moreau and Vincent 2004).
H. breviceps is thought to breed on an approximately monthly cycle throughout the Austral summer, producing 50–100 young per brood (Kuiter 2000). Males have large pouches that they inflate when courting females. In situ observations indicate that adult seahorses display and interact with potential partners, although not every day, and not necessarily with the same partner at each encounter (Moreau and Vincent 2004). Females transfer batches of eggs (1.6 mm diameter (Vincent 1990) to males during copulation which can take from a matter of minutes to 2.5 days, in ex situ conditions (Kuiter 1993). Kuiter (1993) reports that in captivity, males may accept eggs from more than one female, although this has yet to be observed in natural wild pairs. Larvae have been observed swimming to the surface upon release, where they grasp small bits of weed or debris in surface waters (Kuiter 2000). Kuiter (2000) reports size at settlement to be 25 mm.
Longevity in aquaria is at least 3–5 years (P.Quong, pers. comm. in Pogonoski et al. 2002), but lifespan in the wild is unknown.
|Major Threat(s):||The biggest threat facing H. breviceps is likely to be increasing development and population pressure in coastal waters leading to the degradation of shallow inshore habitat (Pogonoski et al. 2002). Such threats remain unquantified for this species at present. Additional threat may be posed by collection for the marine aquarium fish trade, as H. breviceps can be brilliantly coloured (Pogonoski et al. 2002). Current removal rates (estimated at <100 wild caught individuals annually) need to be assessed in light of population abundance data that is not presently available. Prawn trawling in Spencer Gulf South Australia (Tanner 2003) poses an unknown threat to populations and/or habitat.|
Listed as a genus (Hippocampus) on Appendix II of CITES (Convention on International Trade of Endangered Species of Wild Fauna and Flora).
1. All syngnathids are listed as Protected Aquatic Biota in Victoria.
2. The Tasmanian Living Marine Resources Management Act 1995 prohibits the take of all syngnathids in Tasmania (by non-permit holders, since Sept. 1994).
3. All syngnathids are subject to the export controls of the Commonwealth Wildlife Protection (Regulation of Exports and Imports) Act 1982 from 1 January 1998.
4. Australian H. breviceps populations were moved under the Australian Wildlife Protection Act in 1998 and placed under the EPBC Act in 2001.
5. No Australian Society of Fish Biology Listing.
6. Likely to inhabit the Blanche Harbour-Douglas Bank Aquatic Reserve (Marine Protected Areas) in Spencer Gulf, Southern Australia.
|Citation:||Morgan, S.K., Pogonoski, J.J., Pollard, D.A. & Paxton, J.R. 2006. Hippocampus breviceps. The IUCN Red List of Threatened Species 2006: e.T10063A3158537.Downloaded on 23 January 2017.|
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