|Scientific Name:||Mobula japanica|
Cephaloptera japanica Müller & Henle, 1841
Mobula japonica (Müller & Henle, 1841)
Mobula mobular_new (Bonnaterre, 1788)
|Taxonomic Notes:||This species needs to be critically compared to Mobula mobular from the Mediterranean Sea (Compagno and Last 1999). A similar but smaller Mobula species found in eastern Indonesia also needs to be examined (W. White pers. obs.).|
|Red List Category & Criteria:||Near Threatened ver 3.1|
|Assessor(s):||White, W.T., Clark, T.B., Smith, W.D. & Bizzarro, J.J.|
|Reviewer(s):||Kyne, P.M., Notarbartolo-di-Sciara, G., Fowler, S.L. & Compagno , L.J.V. (Shark Red List Authority)|
Mobula japanica is probably circumglobal in all temperate and tropical seas, but its distribution is not completely defined. It is a large devil ray (reaching 310 cm disc width) of inshore, offshore and possibly oceanic environments. Mobula japanica is highly susceptible to gillnets and is known to be landed in Indonesia, México and the Philippines and likely elsewhere across its range. It is a common component of the inshore pelagic tuna gillnet fishery in Indonesia where the flesh and gill rakers are utilised. The high value of gill rakers, which are dried and exported for the Asian medicinal market, has resulted in recent dramatic increases in fishing for mobulids in Indonesia with targeting now occurring. In the Gulf of California, México, the species is also landed when targeted with harpoons and as bycatch from gillnets. In the Philippines the species was historically targeted in a mixed mobulid fishery, and while a ban on fishing for devil rays is presently in place, enforcement is insufficient and landings still occur. Information on catches is not available from other parts of its range, but it is likely being captured elsewhere, certainly in Southeast Asia where target fisheries for whale sharks and manta rays operate. While few species composition data are available (limiting the assessment of current fishing pressures on populations), increased targeting and catches in Indonesia, which may mirror increases elsewhere, is cause for great concern and requires urgent international conservation measures as the species is unlikely to be able to tolerate present levels of exploitation. Its large size and fecundity of a single pup per litter emphasizes the limited reproductive potential and low productivity of this species. Mobula japanica is assessed as Near Threatened globally, but Vulnerable throughout Southeast Asia where catches and demand are increasing. Vulnerable listings may also be warranted elsewhere if future studies show declines in populations where fished.
|Previously published Red List assessments:|
|Range Description:||Possibly circumglobal in temperate and tropical waters. Apart from confirmed occurrences (see Distribution) the species possibly occurs in the North Atlantic (Notarbartolo-di-Sciara 1987) and given its documented occurrence from places such as Fiji and Tuvalu, it is most certainly present in the waters of many countries in the South Pacific. It was only recently confirmed from Australian waters (Kyne et al. 2005).
The southern Gulf of California is believed to serve as an important spring and summer mating and feeding ground for adults (Notarbartolo-di-Sciara 1988). Pupping appears to take place offshore, Ebert (2003) suggesting around offshore islands or seamounts.
Native:Australia (New South Wales, Queensland); Bangladesh; Brazil; Cambodia; China; Colombia; Costa Rica; Côte d'Ivoire; Ecuador; El Salvador; Fiji; Guatemala; Honduras; India; Indonesia; Japan; Korea, Democratic People's Republic of; Korea, Republic of; Mexico; Myanmar; New Zealand; Nicaragua; Oman; Pakistan; Panama; Peru; Philippines; Somalia; South Africa; Sri Lanka; Taiwan, Province of China; Thailand; Tuvalu; United States (California, Hawaiian Is.); Viet Nam; Yemen
|FAO Marine Fishing Areas:|
Atlantic – southwest; Atlantic – eastern central; Indian Ocean – western; Indian Ocean – eastern; Pacific – northwest; Pacific – western central; Pacific – southwest; Pacific – eastern central; Pacific – southeast
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||No information available. Reported as locally common by Compagno and Last (1999), but probably rare in some parts of its range, for example Australia where it has been documented only from two records (Kyne et al. 2005).|
|Current Population Trend:||Unknown|
|Habitat and Ecology:||Information on the biology of Mobula japanica is extremely limited. The species is found inshore, offshore and possibly in oceanic environments, but the movement patterns within its range are little known. Most observations and landings are coastal (Compagno and Last 1999). Notarbartolo-di-Sciara (1988) suggested that this species may be able to tolerate lower water temperatures than other mobulids. Although it is observed in small aggregations, it is not believed to be a schooling species. Size, but not sexual, segregation has been observed within the Gulf of California, México (Notarbartolo-di-Sciara 1988).
Mobula japanica attains at least 310 cm DW but is usually smaller than 250 cm DW. The reproductive mode within this family is aplacental viviparity and the species possesses only a single functional ovary. Embryos obtain nutrients initially by yolk, then through absorption of enriched uterine fluid from the mother (Wourms 1977). Size at birth ranges between 70 and 85 cm DW (Notarbartolo-di-Sciara 1988, Compagno and Last 1999). In Indonesia, males mature between 205 and 210 cm DW, and one pregnant female contained a single embryo 50 cm DW (W. White unpublished data). In the Gulf of California, males appeared to reach sexual maturity at ~210 cm DW and females by ~207 cm DW based on follicle size.
There is no published information on the age and growth of this species.
The species is planktivorous with stomach contents containing 99.6% euphausiids (Nyctiphanes simplex) from April through July (Notarbartolo-di-Sciara 1988).
In the area around Bahia de la Ventana (southern Gulf of California, México) individuals are found from April through late summer, with a peak of abundance in late summer (Notarbartolo-di-Sciara 1988). Seasonally later occurrence than M. thurstoni in the Bahia la Ventana region suggests resource competition avoidance (Notarbartolo-di-Sciara 1988). Movement patterns and migrations of mobulids are not well understood.
Life history parameters
Age at maturity (years): Unknown.
Size at maturity (disc width): Female: Gulf of California: ~207 cm DW (Notarbartolo-di-Sciara 1988); Male: 205 to 210 cm DW (Indonesia) (W. White unpublished data), ~210 cm DW (Gulf of California) (Notarbartolo-di-Sciara 1988).
Longevity (years): Unknown.
Maximum size (disc width): 310 cm DW.
Size at birth: 70 to 85 cm DW (Notarbartolo-di-Sciara 1988, Compagno and Last 1999).
Average reproductive age (years): Unknown.
Gestation time (months): Unknown.
Reproductive periodicity: Unknown.
Average annual fecundity or litter size: 1 pup/litter (W. White unpublished data).
Annual rate of population increase: Unknown.
Natural mortality: Unknown.
Mobula japanica is highly susceptible to gillnets and is taken, either as bycatch or as a target species in Indonesia, México and the Philippines. Juveniles could also be incidentally captured in trawl fisheries. While information is available on these areas it is likely to be landed in other countries also, such as West Africa and particularly in Southeast Asia where pressure on the marine environment is considerable and where mobulid gill rakers are a high value product. It is reported to be taken as longline bycatch in the Gulf of Aden (Bonfil and Abdallah 2004).
Mobula japanica is a common catch in the inshore pelagic tuna gillnet fisheries of Indonesia and is also taken by purse seine in that country. The high value of gill rakers in some areas, e.g., Pelabuhanratu in West Java (W. White unpublished data), is driving a dramatic increase in the catch of mobulids in Indonesia where some fishers are now targeting devil rays. When shark catches are lower (off-season, December to March) fishers are landing more mobulids as an alternative (W. White pers. obs.). The flesh is also utilized both for human consumption and as bait and chum for longlines.
The species is caught in artisanal drift and demersal gillnet fisheries and directly targeted using harpoons in the Gulf of California. Mobula japanica represented 30% of the catch of mobulids observed during a survey of artisanal landings in Bahia de la Ventana, southwestern Gulf of California (Notarbartolo-di-Sciara 1988). This was second to M. thurstoni, which represented 58% of the catch. Mean daily capture of M. japanica in Bahia de la Ventana from March to July 1983 was: March: 0.0, April: 0.4, May: 0.4, June: 1.7, July: 4.3 (Notarbartolo-di-Sciara 1988). Seventeen individuals were noted among landings of 12 pangas at Punta Arena de la Ventana in June 2001 (J. Bizzarro pers. obs.). There is still an active mobulid fishery in the southwest Gulf of California, south of La Paz and devil rays are also landed in nearshore artisanal elasmobranch fisheries throughout the Gulf of California.
Mobula japonica comprised 37% of the Philippine mobulid fishery during 2002 (Bureau of Fisheries and Aquatic Resources, unpublished study), which may reflect its relative importance in other target fisheries in the Southeast Asia region. There is currently a ban on fishing for manta rays in the Philippines, but the effectiveness of this ban is questionable due to limited enforcement ability and mobulids are still being taken illegally.
Mobula japanica is not likely to be able to tolerate high catch levels, given its low reproductive potential. Increasing catches of mobulids in Indonesia, which may mirror increases elsewhere, is of great concern.
Additional research is needed to quantify the extent of target and non-target fisheries take for this species throughout its range. Because of its large size, migratory behavior, extremely low fecundity and large size at maturity, this species is likely highly vulnerable to fishing pressure. However, available life history information is limited and more research is required to make a more accurate assessment of the threat posed by fisheries.
In México, a moratorium on the issue of elasmobranch fishing permits was issued in 1993, but no formal management plan has been implemented for Mobula japanica specifically or most other chondrichthyans. However, legislation is currently being developed in México to establish national elasmobranch fishery management.
Elasmobranch landings in most parts of the world generally lack species-specific details (for example in México, batoids are broadly grouped as "manta raya"). Improved clarity in catch records would provide a basis for detecting potential trends in effort and landings.
In the Philippines, fishing for mobulids was banned in 1998, however it was lifted in 1999 to study the fishery. The ban was put back in place in 2002, and currently it is illegal to fish for any Manta or Mobula in Philippine waters. However, enforcement is insufficient and mobulids are still being taken illegally.
Elasmobranch fisheries are generally unmanaged throughout Central America and Southeast Asia and indeed elsewhere in the range of this species, and attempts to regulate fisheries in these regions would greatly improve conservation of M. japanica and other chondrichthyans.
The development and implementation of management plans (national and/or regional e.g., under the FAO International Plan of Action for the Conservation and Management of Sharks: IPOA-Sharks) are required to facilitate the conservation and sustainable management of all chondrichthyan species across the regions where this ray occurs.
The vulnerability of mobulids and increasing catches requires urgent international conservation measures. These will need to focus on harvest and trade management.
Bonfil, R. and Abdallah, M. 2004. Field identification guide to the sharks and rays of the Red Sea and Gulf of Aden. FAO Species Identification Guide for Fishery Purposes. FAO, Rome.
Compagno, L.J.V. and Last, P.R. 1999. Mobulidae. 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 Linophrynidae). FAO, Rome. p. 1524-1529.
Ebert, D.A. 2003. Sharks, Rays and Chimaeras of California.
IUCN. 2006. IUCN Red List of Threatened Species.
IUCN SSC Shark Specialist Group. Specialist Group website. Available at: http://www.iucnssg.org/.
Kyne, P.M., Johnson, J.W., Courtney, A.J. and Bennett, M.B. 2005. New biogeographical information on Queensland chondrichthyans. Memoirs of the Queensland Museum 50(2):321–327.
Last, P.R. and Stevens, J.D. 1994. Sharks and Rays of Australia. CSIRO, Australia.
Michael, S.W. 1993. Reef Sharks and Rays of the World. A Guide to their Identification, Behavior and Ecology. Sea Challengers, Monterey, California.
Notarbartolo di Sciara, G. 1987. A revisionary study of the genus Mobula Rafinesque, 1810 (Chondrichthyes: Mobulidae) with the description of a new species. Zoological Journal of the Linnean Society 91: 1-91.
Notarbatolo-di-Sciara, G. 1988. Natural history of the rays of the genus Mobula in the Gulf of California. Fishery Bulletin 86(1):45–66.
Paulin, C.D., Habib, G., Carey, C.L., Swanson, P.M. and Vos, G.J. 1982. New records of Mobula japanica and Masturus lanceolatus, and further records of Luvaris imperialis (Pisces: Mobulidae, Louvaridae) from New Zealand. New Zealand Journal of Marine and Freshwater Research 16: 11-17.
Republic of the Philippines, Department of Agriculture. 1998. Ban on the taking or catching, selling, purchasing and possessing, transporting and exporting of Whale Sharks and Manta Rays. Fisheries Administrative Order No.193.
Wourms, J.P. 1977. Reproduction and development in chondrichthyan fishes. American Zoologist 17:379–410.
|Citation:||White, W.T., Clark, T.B., Smith, W.D. & Bizzarro, J.J. 2006. Mobula japanica. The IUCN Red List of Threatened Species 2006: e.T41833A10576180.Downloaded on 29 June 2017.|
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