|Scientific Name:||Hyporthodus mystacinus (Poey, 1852)|
Epinephelus mystacinus Poey, 1852
Epinephelus octofasciatus (non Griffin, 1926)
Hyporthodus mystacinus (Poey, 1852)
Serranus mystacinus Poey, 1852
|Taxonomic Notes:||Misidentified as Hyporthodus octofasciatus based on specimen collected from Japan (Heemstra and Randall 1993). Eastern Pacific population may be a distinct species (Craig and Heemstra, pers. comm.).
A recent publication changed the generic name of this species to Hyporthodus (Craig and Hastings 2007) and a change of family name to Epinephelidae (Smith and Craig 2007).
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor(s):||Rocha, L., Ferreira, B., Choat, J.H., Craig, M. & Sadovy, Y.|
|Reviewer(s):||Sadovy, Y. & Moss, K. (Grouper and Wrasse Red List Authority)|
Based on its deep habitat, and apparent constant catches, Hyporthodus mystacinus is currently not experiencing significant decline, but warrants continued monitoring since little is known of its biology and because it is a target of the commercial fishery. The current assessment of this species is Least Concern.
|Range Description:||Hyporthodus mystacinus occurs in the western Atlantic, where it is found in Bermuda, North Carolina (USA), Florida (USA), Gulf of Mexico, Bahamas, Cuba, Yucatan (Mexico), Jamaica, Puerto Rico, the Virgin Islands, and the Leeward islands to Trinidad. In the eastern Pacific, it is reported from the Galápagos Islands, Paramount Seamount, coastal Ecuador, northeast coast of Brazil south to 22° and Trindade Island.|
Native:Anguilla; Antigua and Barbuda; Bahamas; Barbados; Belize; Bermuda; Cayman Islands; Colombia; Cuba; Dominica; Dominican Republic; Ecuador; Grenada; Guadeloupe; Haiti; Honduras; Jamaica; Mexico; Montserrat; Puerto Rico; Saint Kitts and Nevis; Saint Lucia; Saint Vincent and the Grenadines; Trinidad and Tobago; Turks and Caicos Islands; United States; United States Minor Outlying Islands; Venezuela, Bolivarian Republic of; Virgin Islands, British; Virgin Islands, U.S.
|FAO Marine Fishing Areas:|
Atlantic – western central; Pacific – southeast
|Range Map:||Click here to open the map viewer and explore range.|
Hyporthodus mystacinus was described as "mysterious" and "rarely seen" grouper species (Schobernd 2004).
There are no studies on the abundance except the annual species and abundance survey conducted by novice and expert divers.
Fishery-independent data by country
USA-based on the information from Reef Environmental Education Foundation (REEF), the sighting frequency (SF; a value calculated as dividing the number of survey with Hyporthodus mystacinus encountered [n] by the total number of survey carried out in a particular year [N]) of Hyporthodus mystacinus in tropical western Atlantic ranged from 48.0% to 60.5%, with an average of 0.010% from 1993 to 2005 (www.reef.org/data; accessed on 15th Sep 2006) (Table 1, in Supplementary Material).
See the Supplementary Material for Table 1: sighting frequency of H. mystacinus from underwater visla census by Reef Environmental Education Foundation (REEF).
Bullock and Smith (1991) did not record any Hyporthodus mystacinus during their survey on groupers from the west Florida shelf.
NMFS is the only source on the landings of Hyporthodus mystacinus.
Fishery-dependent data by country
According to NMFS, annual landings of commercial catches of Hyporthodus mystacinus in the USA from 1990 to 2003, the quantity caught stayed relatively low (0.8 to 2.0 metric tonnes) with no data available in 1991 to 1995, 1997 to 1998, 2001 and 2004 to 2005 (www.st.nmfs.gov, accessed on 14th September 2006) (Table 2, in Supplementary Material).
See the Supplementary Material for Table 2: National Marine Fisheries Service (NMFS) commercial catch data 1990-2003.
Commercial landings are minor and there is little recreational take in SE US.
The catch per unit effort for Hyporthodus mystacinus in Brazil was 3.2 fish per 1,000 hooks between 100 to 300 m.
|Current Population Trend:||Stable|
|Habitat and Ecology:||General|
Hyporthodus mystacinus is a bathydemersal species that is typically solitary and occurs from 100 to 400 m. Juveniles sometimes occur in water as shallow as 30 m.
Feeds on fishes, crustaceans, and squids. Virtually nothing is known of the age, growth, and reproduction of this species.
Size and mortality
Hyporthodus mystacinus attains a maximum body weight of 107.0 kg, with male attaining a maximum size of 160 cm TL and females at least 100 cm TL (Appeldorn et al. 1997, Heemstra and Randall 1993). Natural mortality is estimated to be 0.14 (J. McGovern, pers. com.).
Reproduction and maturity
The estimated size at maturity is 81.1 cm (31.9 in), although this may not be accurate (J. McGovern, pers. com). No information is available on its reproductive life history, including spawning and sexual pattern.
Virtually nothing is known of the age and growth of this species (Heemstra and Randall 1993).
|Major Threat(s):||Hyporthodus mystacinus is threatened by both recreational and commercial fisheries (Heemstra and Randall 1993).|
|Conservation Actions:||There are closed areas in the Gulf of Mexico (Madison-Swanson) and South Atlantic (Oculina HAPC) where misty grouper may occur. In addition, Amendment 14 to the Snapper Grouper Fishery Management Plan of the South Atlantic Region will be implemented during 2007. Misty grouper may occur in some of the proposed South Atlantic MPAs.|
Acero, P.A. and Garzon, F.J. 1982. Meros, chernas y cabrillas del caribe Colombiano (Pisces: Serranidae: Epinephelinae: Epinephelini). Caldasia 16((78)): 355-376.
Acero, P.A. and Garzon, F.J. 1982. Un revision de las fichas de identificacion de la FAO para peces Marinos del Atlantico centro-occidental, incluyendo nuevos registros para el cabribe Colombiano. An. Inst. Inv. Mar. 12: 33-39.
Appeldoorn, R.S., Dennis, G.D. and Lopez, O.M. 1987. Review of shared demersal resources of Puerto Rico and the Lesser Antilles region. FAO Fisheries Report No. 338. In: FAO (ed.), FAO Fisheries Report. FAO, Rome, Italy.
Bullock, L.H. and Smith, G.B. 1991. Seabasses (Pisces: Serranidae). Memoirs of the Hourglass Cruises, Volume VIII, Part II..
Craig, M.T. and Hastings, P.A. 2007. A molecular phylogeny of the groupers of the subfamily Epinephelinae (Serranidae) with a revised classification of the Epinephelini. Ichthyological Research 54(1): 1-17.
Heemstra, P.C. and Randall, J.E. 1993. FAO species catalogue. Vol. 16. Groupers of the world (Family Serranidae, Subfamily Epinephelinae). An annotated and illustrated catalogue of the grouper, rockcod, hind, coral grouper and lyretail species known to date. FAO, Rome.
IUCN. 2008. IUCN Red List of Threatened Species. Available at: http://www.iucnredlist.org. (Accessed: 5 October 2008).
Schobernd, Z. 2004. Groupers and Seabasses: Where Do They Live? Available at: http://www.oceanexplorer.noaa.gov/Explorations/04etta/logs/aug26/aug26.html.
Smith, W.L. and Craig, M.T. 2007. Casting the percomorph net widely: The importance of broad taxonomic sampling in the search for the placement of serranid and percid fishes. Copeia 2007(1): 35-55.
|Citation:||Rocha, L., Ferreira, B., Choat, J.H., Craig, M. & Sadovy, Y. 2008. Hyporthodus mystacinus. The IUCN Red List of Threatened Species 2008: e.T132827A3462434.Downloaded on 19 March 2018.|