|Scientific Name:||Actinopyga miliaris|
|Species Authority:||(Quoy & Gaimard, 1833)|
Holothuria miliaris Quoy&Gaimard,1833
Muelleria miliaris (Quoy & Gaimard)
|Red List Category & Criteria:||Vulnerable A2bd ver 3.1|
|Assessor/s:||Conand, C., Purcell, S. & Gamboa, R.|
|Reviewer/s:||Harwell, H., Polidoro, B. & Carpenter, K.E.|
Actinopyga miliaris is commercially exploited throughout its range, and is a medium value species that is relatively easy to collect (e.g. found in higher abundance and on shallow seagrass beds). Its biology is poorly known.. Based on a number of quantitative and qualitative studies, populations are estimated to be depleted and have declined by more than 60-90% in at least 50% of its range since the 1960s, and is considered overexploited in at least 40% of it range although exact declines are difficult to estimate. The status of populations in East Africa are unknown, but it is known to be collected. Declines and overexploitation have occurred primarily since the 1960s, and although generation length is not known, echinoderms are not considered to go through senescence and therefore one generation length is likely greater than several decades. At present, global declines are therefore estimated to be between 30%-40% based on estimates of depletion and overexploitation across its range. A. miliaris is therefore listed as Vulnerable.However, better and more quantitative data are needed to better estimate the impact of fishing on this species. If other shallow water species are continued to be fished out, effort for this species will likely increase even further.
|Range Description:||Actinopyga miliaris is found in the Indo Pacific from east Africa and the Red Sea to India, eastward to northern Australia, north to southern Japan and China, eastward to Fiji, Tuvalu and Tonga, excluding the Persian Gulf and Hawaii. This species can be found throughout the Western Central Pacific between 0-12 m (Kinch et al. 2008a), in Asia (Choo 2008) and in the Africa and Indian Ocean region up to 20 m (Conand 2008).|
Native:American Samoa (American Samoa); Australia; Brunei Darussalam; Cambodia; China; Comoros; Cook Islands; Egypt; Eritrea; Fiji; French Polynesia; Guam; India; Indonesia; Israel; Japan; Jordan; Kenya; Kiribati; Madagascar; Malaysia; Maldives; Marshall Islands; Mauritius; Mayotte; Micronesia, Federated States of ; Mozambique; Myanmar; Nauru; New Caledonia; Northern Mariana Islands; Palau; Papua New Guinea; Philippines; Réunion; Saudi Arabia; Seychelles; Singapore; Solomon Islands; Somalia; Sri Lanka; Sudan; Taiwan, Province of China; Tanzania, United Republic of; Thailand; Tokelau; Tonga; Tuvalu; Vanuatu; Viet Nam; Wallis and Futuna; Yemen
|FAO Marine Fishing Areas:||
Indian Ocean – eastern; Indian Ocean – western; Pacific – northwest; Pacific – western central
|Range Map:||Click here to open the map viewer and explore range.|
Actinopyga miliaris is a relatively common species. However, this species has been heavily depleted over the past 50 years in South East Asia and parts of the South Pacific (India, Viet Nam, Madagascar, Philippines, Indonesia, Papua New Guinea, New Caledonia), which accounts for approximately 50% of its range. The status of the populations in East Africa are unknown but are assumed to be overexploited (40% of its range). Populations in Australia (10% of range) are mostly unknown, and are not yet targeted. Depletion refers to commercially unviable, and is estimated to represent an approximately 60-90% loss or greater over the past 50 years (since the 1960s). Shallow waters are more heavily impacted. In areas where it is considered overexploited, populations are difficult to estimate based on variation in regional and local fishing effort, but harvests have declined and based on traditional fisheries definitions, overexploited is estimated to be 30% above maximum sustainable yield. Populations of Actinopyga mauritiana, A. miliaris and Holothuria scabra appear low and will need to be managed prudently to safeguard stocks from dwindling to levels where they cannot easily be repopulated naturally (Purcell et al. 2009).
Regional and Country Information:
In Vanuatu, there was a relatively high abundance of this species (785 ind./ha) in 1987; however, recent surveys found that densities were low at the island of Efate compared with results from Malekula (Kinch et al. 2008a). In Fiji, Actinopyga miliaris was one of the most important commercial sea cucumbers and occurred at high densities in certain sites; however surveys a decade later found that A. miliaris had a more restricted distribution and lower densities (Kinch et al. 2008).
In Milne Bay, Papua New Guinea, CPUE was <0.1 sea cucumbers/diver/hour. Whilst a joint CPUE for Actinopyga miliaris and A. echinites in Palau showed 68.2 sea cucumbers.diver/hour (Kinch et al. 2008).
In Seychelles, it is among the most abundant species, and it is currently commercially exploited (Aumeeruddy and Conand 2008).
Kalaeb et al. (2008) used transect data to calculate a population density of 157.5 individuals of this species per hectare in near shore waters of Eritrea, east Africa. In Tanzania, there was an increase of bêche-de-mer exports, including this species, from <200 tonnes in 1980s to 617 tonnes in 1992. However, it started to decline afterward. In 1997 Tanzania was exporting 8 tonnes and exporters have stopped due to decline of profit (Conand 2008).
|Habitat and Ecology:||
In the Western Central Pacific Region, Actinopyga miliaris prefers reef flats of fringing reefs and lagoon-islet reefs, rubble reefs and compact flats between 0-12 m (Kinch et al. 2008a). In the Indian Ocean region, it prefers reef flats and seagrass over coral substrate up to 20 m and it does not bury (Conand 2008). In New Caledonia, A. miliaris reproduces twice a year, with one spawning event in May and a second in November and December (Kinch et al. 2008). In China, it prefers areas affected by a strong wave action (Li 2004).
In the Indian Ocean, A. miliaris is common in shallow waters. It is generally found on reef flats of fringing and lagoon-islet reefs between live or dead coral heads, and in sea grass beds, but it is rarely if ever found on barrier reefs. It is commonly distributed on shallow sub-littoral areas with terrigenous influence and coastal reef at a depth range from 0 to 10 m (Rasolofonirina pers comm. 2009).Conand (2008) states that despite high abundance of this species, there is very little biological information.
Generation length is unknown for this species. Body size is not a good indicator of age or longevity. There is some indication, however, that many echinoderms do not go through senescence, but simply regenerate. Therefore generation length cannot be estimated, but is assumed to be greater than several decades in a natural, un-disturbed environment.
Actinopyga miliaris is of small to medium size, with medium commercial value. It is easily collected, and often taken by gleaning. Excessive commercial harvest is a reason for concern in some of its range (Toral-Granda 2006).
Although not one of the most important species (lower medium value species) for fishery purposes, it can be expected that this species may become more popular after the depletion or reduction of other species of higher commercial importance and value. This is as seen in India after the decline of Holothuria scabra and Actinpyga echinites (Conand 2008).
Sea cucumber collection is regulated in some areas, and has been banned elsewhere, including the Andaman and Nicobar Islands (Bruckner et al. 2003). In India, as of 2002 there is a ban on collection, processing and export of all sea cucumbers (Conand 2008). In Fiji, harvest is restricted to Fijian natives, use of scuba gear is forbidden, and catch is restricted by a minimum legal dry length of 7.62 cm for all sea cucumber species (Bruckner et al. 2003).
Since late 2007, there has been a fishery moratorium in Yap for Actinopyga miliaris (Kinch et al. 2008). In PNG, there is a live size limit for A. miliaris of 15 cm TL, and 10 cm TL for dry size; in New Caledonia it is 25 cm TL live and 12 cm TL dry; in Torres Strait (Australia) it is 22 cm TL live size (Kinch et al. 2008). The distribution of A. miliaris also overlaps with several Marine Protected Areas throughout its distribution.
Bruckner, A.W., Johnson, K.A. and Field, J.D. 2003. Conservation strategies for sea cucumbers: Can a CITES Appendix II listing promote sustainable international trade? SPC Beche-de-mer Information Bulletin 18: 24-33.
Chen, J. 2004. Present status and prospects of sea cucumber industry in China. In: A. Lovatelli, C. Conand, S. Purcell, S. Uthicke, J.-F. Hamel and A. Mercier (eds), Advances in Sea Cucumber Aquaculture and Management, pp. 25-38. FAO, Rome.
Choo, P.S. 2008. Population status, fisheries and trade of sea cucumbers in Asia. In: M.V. Toral-Granda, A. Lovatelli, M. Vasconcellos. (ed.), Sea cucumbers. A global review on fisheries and trade.. FAO, Rome.
Conand, C. 2008. Population status, fisheries and trade of sea cucumbers in Africa and the Indian Ocean. In: M.V. Toral-Granada, A. Lovatelli, M. Vasconcellos. (ed.), Sea cucumbers. A global review on fisheries and trade.. FAO, Rome.
Conand, C.P. 1998. Holothurians (sea cucumbers, Class Holothuroidea). In: K.E. Carpenter and V.H. Niem (eds), FAO Species Identification Guide for Fishery Purposes, pp. 1157-1190. Rome.
Hartati, S.T., Wahyuni, I.S. and Badri, U.N. 2005. Jenis-Jenis Teripang Di Indonesia: Sea Cucumber species of Indonesia. Research Institute for Marine Fisheries.
IUCN. 2013. IUCN Red List of Threatened Species (ver. 2013.1). Available at: http://www.iucnredlist.org. (Accessed: 12 June 2013).
James, D.B. 2004. Captive Breeding of the Sea Cucumber Holothuria scabra, from India. In: C. Conand, S. Purcell, S. Uthicke, J.-F. Hamel and A. Mercier (eds), Advances in sea cucumber aquaculture and management, pp. 385-395. FAO, Rome.
Kalaeb, T., Ghirmay, D., Semere, Y. and Yohannes, F. 2008. Status and preliminary assessment of the sea cucumber fishery in Eritrea. SPC Beche de Mer Information Bulletin #27.
Kinch, J., Purcell, S., Uthicke, S. and Friedman, K. 2008. Population status, fisheries and trade of sea cucumbers in the Western Central Pacific. In: V. Toral-Granda and A. Lovatelli and M. Vasconcellos. (eds), Sea cucumbers. A global review of fisheries and trade. Fisheries and Aquaculture Technical Paper. No. 516, pp. 7-55. FAO, Rome.
Li, X. 2004. Fishery and resource management of tropical sea cucumbers in the islands of the South China Sea. In: A. Lovatelli, C. Conand, S. Purcell, S. Uthicke, J.F. Hamel, A. Mercier. (ed.), Advances in sea cucumber aquaculture and management.. FAO, Rome.
Purcell, S.W., Gossuin, H. and Agudo, N.N. 2009. Status and management of the sea cucumber fishery of la Grande Terre, New Caledonia. The WorldFish Center, Penang, Malaysia.
Skewes, T., Haywood, M., Pitchern, R. and Willan, R . 2004. Holothurians. National Oceans Office, Hobart, Australia.
Tesfamichael, K., Ghirmay, D., Semere, Y.and Yohannes, F. 2008. Status and preliminary assessment of the sea cucumber fishery in Eritrea. SPC Beche de Mer Information Bulletin 27: 8-12.
Toral-Granda, V.M. 2006. Fact sheets and identification guide for commercial Sea cucumber species.
Toral-Granda, V.M. 2007. The Biological and Trade Status of Sea Cucumbers in the families Holothuriidae and Stichopodidae. Convention on International Trade in Endangerd Species of Wild Fauna and Flora: 33. The Hague, Netherlands.
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|Citation:||Conand, C., Purcell, S. & Gamboa, R. 2013. Actinopyga miliaris. In: IUCN 2013. IUCN Red List of Threatened Species. Version 2013.2. <www.iucnredlist.org>. Downloaded on 11 December 2013.|
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