|Scientific Name:||Glaucostegus typus|
|Species Authority:||(Anonymous [Bennett], 1830)|
Rhinobatos typus Anonymous [Bennett], 1830
|Red List Category & Criteria:||Vulnerable A2bd+3bd+4bd ver 3.1|
|Assessor/s:||White, W.T. & McAuley, R. (SSG Australia & Oceania Regional Workshop, March 2003)|
|Reviewer/s:||Fowler, S., Kyne, P.M. & Cavanagh, R.D. (Shark Red List Authority)|
Rhinobatos typus is taken by multiple artisanal and commercial fisheries throughout its range both as a target species and as bycatch. Flesh is sold for human consumption in Asia and the fins from large animals fetch particularly high prices, creating a significant incentive for bycatch to be retained. Very little is known about the biology or population status of this species. Given its susceptibility to capture by multiple fishing gear types, including trawl nets, gillnets and hooks and its high value fins, it is probable that numbers have been locally reduced by fishing throughout its range. Local population depletion can be inferred from Indonesia where the target gillnet fishery fleet for rhinids and rhynchobatids has declined significantly, reportedly due to declining catch rates. Therefore, globally this species meets the criteria of Vulnerable A2bd+3bd+4bd due to the apparent population decline outlined above and the remaining very high level of exploitation in South East Asia. Furthermore, destruction of habitat, e.g., mangrove areas, and high level of fishing pressure in areas such as Papua (e.g., Merauke) may be having a deleterious effect on juveniles of this species that utilize such inshore regions.
There are no target fisheries for R. typus in Australia but it is a known bycatch of demersal trawl fisheries in the region. The introduction of Turtle Exclusion Devices (TEDs) in the Australian Northern Prawn Trawl Fishery in 2000 and the implementation of various elasmobranch-finning prohibitions, has probably led to a recent reduction in captures by this sector. However, given the population declines throughout South East Asia and the high value placed on fins (even in Australia) the Australian population may meet the criteria of Vulnerable A2d, but more detailed catch data is required and it is thus assessed as Near Threatened in Australian waters.
|Range Description:||Rhinobatos typus is widely distributed in the Indo-Pacific (Last and Stevens 1994, Compagno and Last 1999). Another species, Rhinobatos granulatus, co-occurs with this species at the western extremity of its range but has not been positively identified from the Australia and Oceania Region (Last and Stevens 1994).|
Native:Australia (New South Wales, Northern Territory, Queensland, Western Australia); Bangladesh; India; Indonesia; Malaysia; Singapore; Sri Lanka; Viet Nam
|FAO Marine Fishing Areas:||
Indian Ocean – eastern; Indian Ocean – western; Pacific – southwest; Pacific – western central
|Range Map:||Click here to open the map viewer and explore range.|
|Habitat and Ecology:||
Juveniles of Rhinobatos typus occur inshore, e.g., mangrove systems and estuaries, and around atolls, whilst adults are found in the deeper waters of the continental shelf to about 100 m (Last and Stevens 1994). This species has also been reported to be able to live and breed permanently in freshwater.
Rhinobatos typus is reported to attain at least 270 cm in length (Last and Stevens 1994). Although no published information is available on size at maturity and reproductive biology of this species, specimens examined from Shark Bay (Western Australia) showed that females and males appear to mature at between 155 and 175 cm total length (TL), and young are born at approximately 38 to 43 cm TL (W. White, unpublished data). There does not appear to be a distinct seasonal reproductive cycle with newborn young found in most months of the year (W. White, unpublished data).
This species is a major predator of crustaceans, with an examination of the diets showing that more than 90% of food ingested belongs to juveniles of either the blue swimmer crab (Portunus pelagicus) or the western king prawn (Melicertus latisulcatus) (W. White, unpublished data). Juveniles also utilize shallow sand flats as nursery areas and move into mangrove areas and sand flats at high tide to feed.
There is no published information on the age at maturity, longevity and natural mortality of this species.
The fins from Rhinobatos typus are widely considered as being amongst the most valuable of elasmobranchs (i.e., white-fin) and there is a significant incentive for fishers to remove the fins from large individuals when they are taken as either target catch or bycatch. R. typus is commonly landed as bycatch in fisheries in Indonesia (Bentley 1996, Chen 1996, W. White personal observation). Fisheries targeting the rhynchobatids in eastern Indonesia, e.g., Aru Islands and Merauke (Papua), often catch this species but generally in low numbers.
Since juveniles of this species inhabit shallow sand flats and mangrove estuaries (Last and Stevens 1994, W. White unpubl. data), intensive fishing pressures, e.g., gill, trap and seine nets, in such inshore areas throughout Indonesia, e.g., Merauke (Papua), are most likely having a high level of impact on this species.
Such threats to this species in the Australia and Oceania region appear to be more confined to eastern Indonesia (e.g., Papua). There are no target fisheries for R. typus in Australia but it is a known bycatch of demersal trawl fisheries in the region (Stobutzki et al. 2000, Stephenson and Chidlow in prep.). In northern Australia, this species constitutes a minor component of the catch in the northern prawn trawl fishery and since the introduction of compulsory turtle excluder devices (TEDs) in this fishery in the year 2000, the number of large individuals of such elasmobranchs retained have been further reduced (Stobutzki et al. 2002). There is also likely to be only limited fishing pressure on juvenile R. typus in inshore regions in northern Australia.
|Conservation Actions:||Further research into the population structure, biology and ecology of Rhinobatos typu is required to assess the extent to which fishing pressure, particularly in relation to finning, and habitat destruction is influencing this species within its range. Improved species composition data from all fisheries that take shovelnose rays and guitarfish is necessary.|
Bentley, N. 1996. A Preliminary Survey of Shark Fisheries in Indonesia. Unpublished TRAFFIC Southeast Asia Field Report.
Chen, H.K. (ed.) 1996. Shark Fisheries and the Trade in Sharks and Shark Products in Southeast Asia. TRAFFIC Southeast Asia Report, Petaling Jaya, Selangor, Malaysia
Compagno, L.J.V. and Last, P.R. 1999. Rhinobatidae. In: K.E. Carpenter and V.H.Niem (eds) FAO species identification guide for fishery purposes. The living marine resources of the Western Central Pacific. Volume 3. Batoid fishes, chimaeras and bony fishes part 1 (Elopidae to Linophyrnidae). FAO, Rome, pp. 1423-1430.
IUCN. 2003. 2003 IUCN Red List of Threatened Species. www.iucnredlist.org. Downloaded on 18 November 2003.
IUCN SSC Shark Specialist Group. Specialist Group website. Available at: http://www.iucnssg.org/.
Last, P.R. and Stevens, J.D. 1994. Sharks and Rays of Australia. CSIRO, Australia.
Stevenson, P and Chidlow, J.A. In prep. By-catch in the Pilbara Trawl Fishery. Draft report to Environment Australia. Department of Fisheries, Perth, WA.
Stobutzki, I.C., Miller, M.J., Heales, D.S. and Brewer, D.T. 2002. Sustainability of elasmobranches caught as bycatch in a tropical prawn (shrimp) trawl fishery. Fishery Bulletin 100: 800-821.
|Citation:||White, W.T. & McAuley, R. (SSG Australia & Oceania Regional Workshop, March 2003) 2003. Glaucostegus typus. In: IUCN 2013. IUCN Red List of Threatened Species. Version 2013.2. <www.iucnredlist.org>. Downloaded on 11 March 2014.|
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