|Scientific Name:||Himantura undulata|
|Species Authority:||(Bleeker, 1852)|
Until recently Bleeker’s Variegated Whipray (Himantura undulata) included the recently described species, the Leopard Whipray (H. leoparda) (Last and Stevens 1994, 2009). These two species are often confused with the Reticulate Whipray (H. uarnak) and the Honeycomb Whipray (H. fava) (White et al. 2006). All of these whiprays are from the ‘uarnak’ species-complex, a subgroup of mainly reticulated, ocellated or spotted whiprays. Bleeker’s Variegated Whipray juveniles of 50 cm disc width (DW) have a well developed main denticle band with inconspicuous primary denticles while the adults have a strong pattern of large ocelli and reticulations. Conversely, adults of the Reticulate Whipray have fine reticulations and small black spots, the Leopard Whipray have leopard like markings, while the Honeycomb Whipray have honeycomb reticulations that are widely spaced (White et al. 2006, Manjaji-Matsumoto and Last 2008).
Taxonomic work is currently ongoing to more clearly define the sister species relationships among the ‘uarnak’ species-complex (Peter Last pers. comm. 2010). Manjaji (2004) considers Bleeker’s Variegated Whipray to be a senior synonym of the Honeycomb Whipray (Manjaji-Matsumoto and Last 2008).
|Red List Category & Criteria:||Vulnerable A2cd+3cd+4cd ver 3.1|
|Reviewer(s):||Kyne, P.M. & Ebert, D.A.|
Bleeker’s Variegated Whipray (Himantura undulata) is possibly widely distributed in the Indo-West Pacific in mainly coastal inshore waters. It occurs in the Indo-West Pacific from India to eastern Indonesia, however ongoing taxonomic issues are being investigated; the outcomes of which may affect the known distributional range. Its biology is poorly known, partly due to confusion with other members of the ‘uarnak’ species-complex. This species is commercially valuable; throughout Southeast Asia and parts of the Indian Ocean it is taken as utilised bycatch of a range of commercial and artisanal fisheries including demersal trawl and tangle/gill nets, dropline and longline fisheries and Danish seine fisheries. In recent decades, demersal fishing pressure has increased in both capacity and effort and is intense throughout this species’ inshore range in Southeast Asia and parts of the Indian Ocean. Fishing pressure is also very heavy in the Arafura Sea region; previously more than 600 trawlers operated and although the numbers of currently active trawlers is unclear, there are still high levels of Indonesian trawl fishing in the area. This level of exploitation is of great concern to the sustainability of Bleeker’s Variegated Whipray populations in the Arafura Sea. This species’ preference for inshore coastal waters means it is also threatened by extensive habitat degradation and destructive fishing practices throughout a large part of its range. Although species-specific data are not available, given the species’ high levels of exploitation, extensive habitat degradation and its large size, significant population declines are suspected to have occurred and are likely to be ongoing across large areas of its range.
The species is assessed as Vulnerable on the basis of suspected declines as a result of high levels of exploitation and habitat degradation in large areas of its range. This assessment should be revisited if and when there is any new taxonomic information and/or distributional information as this may affect the fishing pressure to which this species is exposed.
Bleeker’s Variegated Whipray occurs in the Indo-West Pacific from India to eastern Indonesia, though its distribution is poorly defined as this range is based on current knowledge of this species. There are ongoing taxonomic issues that are being investigated and the outcomes of these may affect the known distributional range. There are no confirmed records of this species from Australia (Last and Stevens 2009, Last et al. 2010).
Native:Cambodia; China; India; Indonesia; Malaysia; Myanmar; Thailand; Viet Nam
|FAO Marine Fishing Areas:||
Indian Ocean – eastern; Pacific – northwest; Pacific – western central
|Range Map:||Click here to open the map viewer and explore range.|
This species is caught regularly in Indonesia, but rarely in Malaysia (Manjaji and White 2004). There is no species-specific information about populations or trends, however in a large part of its range there is heavy fishing pressure and extensive habitat degradation, and it is suspected that significant population declines have occurred and are ongoing.
|Habitat and Ecology:||
Bleeker’s Variegated Whipray is demersal on inshore soft substrates (Last et al. 2010). The biology of this species is poorly known, partly due to confusion with other species of the ‘uarnak’ species-complex. This is a large whipray that attains at least 130 cm disc width (DW), is born at around 26–27 cm DW with males maturing at 60–70 cm DW. Reproduction is viviparous with histotrophy and the diet is unknown but likely comprises small fishes and crustaceans (Last et al. 2010).
As there is no information on this species’ maximum age and age at maturity, generation length was inferred as 20 years based on data for the congener, the Blackspotted Whipray (Himantura astra). Female Blackspotted Whipray are reported to have a maximum age of 29 years and an age at maturity of nine years (Jacobsen and Bennett 2010). These were used to calculate a generation length of 19 years based on the equation: generation length = (((29-9)/2)+9). The maximum size of Bleeker’s Variegated Whipray is considerably larger (~130 cm DW) than that of the Blackspotted Whipray (80 cm DW) so it is possible the generation length of Bleeker’s Variegated Whipray could be greater than 20 years.
|Use and Trade:||
This species is used for its meat and possibly also for its cartilage and high value skin (Last et al. 2010).
The threats to Bleeker’s Variegated Whipray are many of those faced by other Himantura species within its range. Bleeker’s Variegated Whipray may be more vulnerable than some of its congeners due to its large size at maturity and maximum size and its preference for inshore coastal waters that are heavily fished and degraded in many parts of its range (Manjaji and White 2004).
In recent decades, demersal fishing pressure has increased in both capacity and effort in many areas of this species’ inshore range. For example, demersal resources in the Gulf of Thailand went from being lightly exploited to severely over-exploited between 1973 and 1994 (Pauly et al. 2005). On standardized trawl surveys conducted over this 20 year period in the Gulf of Thailand, the abundance (biomass) of the major trawl bycatch groups was recorded. The group ‘rays’ showed a large reduction in biomass over this period and an ecosystem model fitted to the bycatch data indicated that ‘rays’ were one of the groups most severely impacted by the initial increase in fishing pressure (Pauly et al. 2005). Species-specific catch data are not available, but Indonesian landings of ‘Rays, stingrays, mantas, nei’ (nei = not elsewhere included) increased from ~10,000 t in 1975 to 58,000 t in 2004 (FAO 2009).
|Conservation Actions:||Research is required to assess catches of Bleeker's Variegated Whipray throughout its range, and to examine its habitat, ecology and life history parameters including confirmation of its distributional range. The fisheries that capture this species are largely unregulated (licenses are issued but catches and landings are not properly monitored), and presently there are no specific conservation actions in place to help address this problem.|
Bleeker, P. 1852. Bijdrage tot de kennis der Plagiostomen van den Indischen Archipel. Verh. Batav. Genootsch. Kunst. Wet. 24(12): 1-92.
FAO. 2007. The World's Mangroves 1980-2005. FAO Forestry Paper 153. Forestry Department, Food and Agriculture Organization of the United Nations (FAO), Rome.
FAO. 2009. Fishstat online database. Global Capture Production. Available at: http://www.fao.org/fishery/statistics /global-capture-production. (Accessed: 29 March 2010).
Heazle, M. and Butcher, J.G. 2007. Fisheries depletion and the state in Indonesia: Towards a regional regulatory regime. Marine Policy 31: 276-286.
IUCN. 2012. IUCN Red List of Threatened Species (ver. 2012.1). Available at: http://www.iucnredlist.org. (Accessed: 19 June 2012).
Last, P.R. and Stevens, J.D. 1994. Sharks and Rays of Australia. First Edition. CSIRO Publishing, Collingwood, Australia.
Last, P.R. and Stevens, J.D. 2009. Sharks and Rays of Australia. Second Edition. CSIRO Publishing, Collingwood, Australia.
Last, P.R., White, W.T., Caira, J.N., Dharmadi, Fahmi, Jensen, K., Lim, A.P.K., Manjaji-Matsumoto, B.M., Naylor, G.J.P., Pogonoski, J.J., Stevens, J.D., Yearsley, G.K. 2010. Sharks and Rays of Borneo. CSIRO Marine and Atmospheric Research, Collingwood.
Manjaji, B.M. 2004. Taxonomy and phylogenetic systematic of the stingray genus Himantura (Family Dasyatidae). PhD. in Zoology Dissertation, University of Tasmania.
Manjaji, B.M. and White, W.T. 2004. Himantura undulata. IUCN 2010. IUCN Red List of Threatened Species. Version 2010.4. Available at: www.iucnredlist.org. (Accessed: 14 February 2011).
Manjaji-Matsumoto, B.M. and Last, P.R. 2008. Himantura leoparda sp. nov., a new whipray (Myliobatoidei: Dasyatidae) from the Indo-Pacific. In: Last, P.R., White, W.T. and Pogonoski, J.J. (eds), Descriptions of new Australian Chondrichthyans, pp. 293-301. CSIRO Marine and Atmospheric Research Paper No 022.
Northern Territory Government. 2009. Fishery Status Reports 2008. Fishery Report No. 101. Department of Resources, 171 pp.
Pauly, D., Booth, S., Christensen, V.W.L., Close, C., Kitchingman, A., Palomares, M.L.D., Watson, R. and Zeller, D. 2005. On the Exploitation of Elasmobranchs, with Emphasis on Cowtail Stingray Pastinachus sephen (Family Dasyatidae). Fisheries Centre: The University of British Columbia Working Paper Series. Fisheries Centre: The University of British Columbia.
White, W.T. and Dharmadi. 2007. Species and size compositions and reproductive biology of rays (Chondrichthyes, Batoidea) caught in target and non-target fisheries in eastern Indonesia. Journal of Fish Biology 70: 1809-1837.
White, W.T., Last, P.R., Stevens, J.D., Yearsley, G.K., Fahmi and Dharmadi. 2006. Economically Important Sharks and Rays of Indonesia. Australian Centre for International Agricultural Research, Canberra, Australia.
|Citation:||Rigby, C. 2012. Himantura undulata. The IUCN Red List of Threatened Species. Version 2014.2. <www.iucnredlist.org>. Downloaded on 17 September 2014.|
|Feedback:||If you see any errors or have any questions or suggestions on what is shown on this page, please fill in the feedback form so that we can correct or extend the information provided|