|Scientific Name:||Acanthurus nigricans|
|Species Authority:||(Linnaeus, 1758)|
Acanthurus aliala Lesson, 1831
Acanthurus glaucoparecius Cuvier, 1829
Acanthurus glaucopareius Cuvier, 1829
Chaetodon nigricans Linnaeus, 1758
|Taxonomic Notes:||Acanthurus nigricans is a member of the A. achilles species complex known for their propensity to hybridize (Randall and Frische 2000). The four species in this complex (A. achilles Shaw, A. japonicus Schmidt, A. leucosternon Bennett, and A. nigricans) are thought to hybridize when their distributional ranges overlap (Craig 2008). Hybrids have been recorded from the Hawaiian Islands (Acanthurus achilles x nigricans), Taiwan (Acanthurus japonicus x nigricans), Indonesia, Christmas and Cocos Island (Acanthurus leucosternon x nigricans) (Randall 2001a, Marie et al. 2007).|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor(s):||Choat, J.H., Abesamis, R., Clements, K.D., McIlwain, J., Myers, R., Nanola, C., Rocha, L.A., Russell, B. & Stockwell, B.|
|Reviewer(s):||Davidson, L., Edgar, G. & Kulbicki, M.|
Acanthurus nigricans is widespread throughout the Pacific Ocean. It is common and abundant in parts of its range. It is caught incidentally as food and is a component of the marine aquarium trade. Harvest for the aquarium trade is not considered a major threat globally and it occurs in a number of marine reserves in parts of its distribution. It is therefore listed as Least Concern.
Acanthurus nigricans is widely distributed in the Pacific Ocean. In the Pacific Ocean, it occurs from Ryukyu islands and the Great Barrier Reef to the Hawaiian islands and French Polynesia (excluding Rapa). In the eastern Indian Ocean, it is known from Cocos-Keeling Islands and Christmas Island. It was recently recorded from Diego Garcia, Chagos Archipelago (Craig 2008).
This species occurs across the eastern Pacific barrier from the tip of Baja California to the southwest and southeast Gulf of California, southern Mexico, Costa Rica to Ecuador and all the offshore islands.
Native:American Samoa (American Samoa); Australia; British Indian Ocean Territory (Chagos Archipelago); Brunei Darussalam; China; Christmas Island; Cocos (Keeling) Islands; Colombia; Cook Islands; Costa Rica; Disputed Territory (Paracel Is., Spratly Is.); Ecuador (Ecuador (mainland), Galápagos); Fiji; French Polynesia; Guam; Indonesia; Japan; Kiribati (Gilbert Is., Kiribati Line Is., Phoenix Is.); Malaysia; Marshall Islands; Mexico; Micronesia, Federated States of ; Nauru; New Caledonia; Niue; Northern Mariana Islands; Palau; Panama; Papua New Guinea; Philippines; Samoa; Singapore; Solomon Islands; Taiwan, Province of China; Thailand; Timor-Leste; Tokelau; Tonga; Tuvalu; United States (Hawaiian Is.); United States Minor Outlying Islands (Howland-Baker Is., Johnston I., Midway Is., US Line Is., Wake Is.); Vanuatu; Viet Nam; Wallis and Futuna
|FAO Marine Fishing Areas:||
Indian Ocean – western; Indian Ocean – eastern; Pacific – eastern central; Pacific – northwest; Pacific – southeast; Pacific – western central
|Lower depth limit (metres):||67|
|Range Map:||Click here to open the map viewer and explore range.|
Acanthurus nigricans is common and widespread throughout the Pacific Ocean. On Christmas Island, it is the dominant Acanthurid on a reef dominated by Acanthurids and achieves mean densities of 83.6 (SE 9.14) per 1,000 m2 (Choat unpub. data). It was at least eightfold more abundant than Acanthurus leucosternon and twofold more abundant than putative hybrids at Cocos (Keeling) and Christmas Island (Marie et al. 2007).
In Fagatale Bay, American Samoa, it is a dominant species on the reef slope (Green et al. 1999). A. nigricans was the second most dominant species recorded from Tutuila, Aunuu, and Taema Banks, American Samoa, contributing to 7.6% of total fish biomass and 11.87% of numerical abundance (Sabater and Tofaeono 2006). In Tutuila Island, American Samoa, it was the second most dominant species recorded, contributing
to 8% of total fish biomass (Sabater and Tofaeono 2007).
It was the fourth most abundant Acanthurid in Guam and Saipan, but makes a minor contribution to the Acanthurid fishery, 2.5% and 0.5% respectively (J. McIlwain unpub. data). This species is collected as an aquarium fish in West Hawaii. The total number of individuals caught from FY 2005-2009 was 3,969 with a total value of $18,813 (Walsh et al. 2010). It is common and locally abundant in the Philippines but is not specifically targeted in the fishery (R. Abesamis and B. Stockwell pers. comm. 2010). It was recorded as generally rare, but locally common, particularly at Louisiades, Milne Bay, Papua New Guinea (Allen 2003). It was recorded as occasional at Raja Ampat, Indonesia (Allen 2003b).
In the central Philippines, density and biomass of herbivorous fish in reserves had positive relationships with duration of reserve protection. Acanthuridae and Labridae (parrotfishes) were the major families that increased in biomass inside reserves with duration of reserve protection. Herbivore biomass inside reserves compared to fished sites was on average 1.4, 4.8 and 8.1 times higher at 0.5 to 4, 5 to 7 and 8 to 11 years of protection, respectively. For A. nigricans, mean biomass recorded in 2 reserves (5 to 7 years duration of protection) were 0.59 and 0.07 (kg per 500 m2) (Stockwell et al. 2009).
This species is the least abundant of the Acanthurids at Gorgona, Colombia. According to Robertson and Allen (1996), this fish was frequent enough to have a resident population in Clipperton Atoll. This fish was studied in the Galapagos archipelago, with an overall mean density of 1.49 ind/500 m2 (Edgar et al. 2004). It is locally common in southern Costa Rica, and in Cano Island and Cocos Island.
According to Aburto-Oropeza and Balart (2001), A. nigricans is a rare species in Los Islotes, Gulf of California, having an occurrence frequency below 10%. In Cabo Pulmo, Gulf of California, this species was considered scarce, with a relative frequency between 25-50% (Villarreal-Cavazos et al. 2000). Densities on the tropical eastern Pacific offshore islands are much higher than along the continental coast.
|Current Population Trend:||Stable|
|Habitat and Ecology:||This reef-associated species inhabits hard substrate areas of clear lagoons and seaward reefs, from the lower surge zone to at least 67 m. Small juveniles hide among large corals (Kuiter and Tonozuka 2001). In the Gulf of Chiriqui, Panama, this species can be found over exposed shallow rocky reefs and deep rocky walls (Dominici-Arosemena and Wolff 2006). According to Rubio (1986), at Gorgona Island, Colombia, this fish (cited as A. glaucopareius) is abundant on rocky substrata, while also frequently found on sandy and coralline substrata. It grazes on algal turf mainly on thallate and filamentous algae (Choat et al. 2002, Choat et al. 2004). Maximum age was 34 years in the Great Barrier Reef (Choat and Robertson 2002). Mean maximum age for females is 30 years, males at 24 years (Jones 2008).
The sexes are separate among the acanthurids and there is no evidence of sexual dimorphism (Reeson 1983). However, there is size dimorphism with females consistently larger than males (J.H. Choat pers. comm. 2010). Acanthurus nigricans is monogamous (Whiteman and Côté 2004).
|Use and Trade:||Acanthurus nigricans is important to subsistence fisheries and is also collected for the aquarium trade (Global Marine Aquarium Database accessed 19 March 2010). Online prices range from $33.98-$99.00 (L. Rocha pers. comm. 2010).|
There are no major threats known for this species.
Surgeonfishes show varying degrees of habitat preference and utilization of coral reef habitats, with some species spending the majority of their life stages on coral reef while others primarily utilize seagrass beds, mangroves, algal beds, and /or rocky reefs. The majority of surgeonfishes are exclusively found on coral reef habitat, and of these, approximately 80% are experiencing a greater than 30% loss of coral reef area and degradation of coral reef habitat quality across their distributions. However, more research is needed to understand the long-term effects of coral reef habitat loss and degradation on these species' populations. Widespread coral reef loss and declining habitat conditions are particularly worrying for species that recruit into areas with live coral cover, especially as studies have shown that protection of pristine habitats facilitate the persistence of adult populations in species that have spatially separated adult and juvenile habitats (Comeros-Raynal et al. 2012).
|Conservation Actions:||There are no species-specific conservation measures in place for this species. Its distribution overlaps several marine protected areas in parts of its range.|
Aburto-Oropeza, O. and Balart, E.F. 2001. Community structure of reef fish in several habitats of a rocky reef in the Gulf of California. Marine Ecology 22(4): 283-305.
Allen, G.R. 2003. Appendix 5. List of the reef fishes of Milne Bay Province, Papua New Guinea. In: G.R. Allen, J.P. Kinch, S.A. McKenna, and P. Seeto (eds), A Rapid Marine Biodiversity Assessment of Milne Bay Province, Papua New Guinea–Survey II (2000), pp. 172. Conservation International, Washington, DC, USA.
Allen, G.R. 2003b. Appendix 1. List of the Reef Fishes of the Raja Ampat Islands. In: R. Donnelly, D. Neville and P.J. Mous (eds), Report on a rapid ecological assessment of the Raja Ampat Islands, Papua, Eastern Indonesia, held October 30 – November 22, 2002. The Nature Conservancy - Southeast Asia Center for Marine Protected Areas, Sanur, Bali.
Choat, J.H. and Robertson, D.R. 2002a. Age-based studies on coral reef fishes. In: P.F. Sale (ed.), Coral reef fishes: dynamics and diversity in a complex ecosystem, pp. 57-80. Academic Press.
Choat, J.H., Clements, K.D. and Robbins, W.D. 2002b. The trophic status of herbivorous fishes on coral reefs. 1. Dietary analyses. Marine Biology 140: 613-623.
Choat, J.H., Robbins, W.D. and Clements, K.D. 2004. The trophic status of herbivorous fishes on coral reefs. Marine Biology 145: 445-454.
Comeros-Raynal, M.T., Choat, J.H., Polidoro, B.A., Clements, K.D., Abesamis, R., Craig, M.T., Lazuardi, M.E., McIlwain, J., Muljadi, A., Myers, R.F., Nañola Jr., C.L., Pardede, S., Rocha, L.A., Russell, B., Sanciangco, J.C., Stockwell, B., Harwell, H. and Carpenter, K.E. 2012. The likelihood of extinction of iconic and dominant components of coral reefs: the parrotfishes and surgeonfishes. PLoS ONE http://dx.plos.org/10.1371/journal.pone.0039825.
Craig, M.T. 2008. The goldrim surgeonfish (Acanthurus nigricans; Acanthuridae) from Diego Garcia, Chagos Archipelago: first record for the central Indian Ocean. Zootaxa 1850: 65-68.
Dominici-Arosemena, A. and Wolff, M. 2006. Reef fish community structure in the Tropical Eastern Pacific (Panamá): living on a relatively stable rocky reef environment. Helgoland Marine Research 60: 287-305.
Edgar, G.J., Banks, S., Fariña, J.M., Calvopiña, M. and Martínez, C. 2004. Regional biogeography of shallow reef fish and macro-invertebrate communities in the Galapagos archipelago. Journal of Biogeography 31(7): 1107-1124.
Global Marine Aquarium Database. 2010. Species Trade Details. Available at: http://www.unep-wcmc.org/GMAD/species.cfm. (Accessed: March 19).
Green, A.L., Birkeland, C.E. and Randall, R.H. 1999. Twenty Years of Disturbance and Change in Fagatale Bay National Marine Sanctuary, American Samoa. Pacific Science 53(4): 376-400.
IUCN. 2012. IUCN Red List of Threatened Species (ver. 2012.2). Available at: http://www.iucnredlist.org. (Accessed: 17 October 2012).
Jones, R. 2008. Reproduction, Growth and Age within Acanthurids: Species that Defy the Trends. School of Marine and Tropical Biology, James Cook University.
Kuiter, R.H. and Tonozuka, T. 2001. Pictorial guide to Indonesian reef fishes. Part 3. Jawfishes - Sunfishes, Opistognathidae - Molidae. Zoonetics, Australia.
Marie, A.D., van Herwerden, L., Choat, J.H. and Hobbs, J.P.A. 2007. Hybridization of reef fishes at the Indo-Pacific biogeographic barrier: a case study. Coral Reefs 26: 841-850.
Randall, J.E. 2001a. Surgeonfishes of the world. Mutual Publishing and Bishop Museum Press, Hawai'i, Honolulu, Hawaii.
Randall, J.E. and Frische, J. 2000. Hybrid Surgeonfishes of the Acanthurus achilles Complex. Aqua: Journal of Ichthyology and Aquatic Biology 4(2): 51-56.
Reeson, P.H. 1983. The biology, ecology and bionomics of the surgeonfishes, Acanthuridae. In: J.L. Munro (ed.), Caribbean coral reef fishery resources, pp. 178-190.
Robertson, D.R. and Allen, G.R. 1996. Zoogeography of the shorefish fauna of Clipperton Atoll. Coral Reefs 15(2): 121-131.
Robertson, D.R. and Allen, G.R. 2006. Shorefishes of the Tropical Eastern Pacific: an information system. Smithsonian Tropical Research Institute.
Rubio, E.A. 1986. Notas sobre la ictiofauna de la isla Gorgona Pacifico Colombiano. Boletin Ecotropica 13: 86-112.
Sabater, M. G. and Tofaeono, S. 2007. Effects of scale and benthic composition on biomass and trophic group distribution of reef fishes in American Samoa. Pacific Science 61: 503-520.
Sabater, M.G. and Tofaeono, S.P. 2006. Spatial variation in biomass, abundance, and species composition of "key reef species" in American Samoa. A technical report submitted by the Key Reef Species Program to Department of Marine and Wildlife Resources (DMWR). This study is funded by the Sportfish Restoration Grant under Federal Aid of the US Fish and Wildlife Service. Department of Marine and Wildlife Resources (DMWR).
Stockwell, B., Jadloc, C.R.L., Abesamis, R.A., Alcala, A.C. and Russ, G.R. 2009. Trophic and benthic responses to no-take marine reserve protection in the Philippines. Marine Ecology Progress Series 389: 1-15.
Villarreal-Cavazos, A., Reyes-Bonilla, H., Bermúdez-Almada, B. and Aripes-Covarrubias, O. 2000. Los peces del arrecife de Cabo Pulmo, Golfo de California, México: Lista sistemática y aspectos de abundancia e biogeografía. Revista de Biología Tropical 48(2-3): 413-424.
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|Citation:||Choat, J.H., Abesamis, R., Clements, K.D., McIlwain, J., Myers, R., Nanola, C., Rocha, L.A., Russell, B. & Stockwell, B. 2012. Acanthurus nigricans. The IUCN Red List of Threatened Species 2012: e.T177969A1506081. . Downloaded on 05 May 2016.|
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