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Description |
Indo-Pacific: Red Sea to South Africa (Ref. 35918) and to the Tuamoto Islands, north to the Ryukyu Islands, south to New Caledonia. Formerly known as Vulnerable (A1d+2cd) (Y. Sadovy) but now listed as Endangered in IUCN 2004 and listed in Appendix II of
Geographic Range [top]
Range Description: The Humphead Wrasse is widely distributed on coral reefs and inshore habitats throughout much of the tropical Indo-Pacific, from western Indian Ocean and Red Sea to southern Japan, New Caledonia and into the central Pacific Ocean (see the Supplementary Material for a distribution map). In Australia, it occurs on offshore reefs of north-western Australia and the Great Barrier Reef (Pogonoski et al. 2002). It is rare in the southern part of the Great Barrier Reef in the Capricorn-Bunker Group (Russell 1983) and at Middleton and Elizabeth Reef (Gill and Reader 1992). This species appears to occur predominantly at depths of less than 100 m. It is not known from the Hawaiian Islands, Johnston Island, Easter Island, Pitcairn Is., Rapa or Lord Howe Islands, Kermadec or Australes Is., and evidently does not occur in the Gulf of Oman, the Persian Gulf, Reunion Is., Mauritius or Rodrigues Is.
Adults are known to occur largely on outer reef areas, often in association with channels and passes. Spawning aggregation sites have been reported from outer reef areas.
For further information about this species, see 4592_Cheilinus_undulatus.pdf.
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Countries occurrence:
Native:
American Samoa (American Samoa); Australia (Ashmore-Cartier Is., Lord Howe Is., Queensland); British Indian Ocean Territory (Chagos Archipelago); Cambodia; China; Christmas Island; Cocos (Keeling) Islands; Comoros; Cook Islands; Disputed Territory (Paracel Is., Spratly Is.); Djibouti; Egypt; Eritrea; Fiji; French Polynesia (Tuamotu); Guam; Hong Kong; India (Laccadive Is.); Indonesia; Israel; Japan (Nansei-shoto); Kenya; Kiribati (Gilbert Is., Kiribati Line Is.); Madagascar; Malaysia; Maldives; Marshall Islands; Mayotte; Micronesia, Federated States of ; Mozambique; Myanmar; Nauru; New Caledonia; Niue; Northern Mariana Islands; Palau; Papua New Guinea; Philippines; Pitcairn; Samoa; Saudi Arabia; Seychelles; Singapore; Solomon Islands; Somalia; Sri Lanka; Sudan; Taiwan, Province of China; Tanzania, United Republic of; Thailand; Timor-Leste; Tokelau; Tonga; Tuvalu; United States Minor Outlying Islands (Wake Is.); Vanuatu; Viet Nam; Wallis and Futuna; Yemen
FAO Marine Fishing Areas:
Native:
Indian Ocean – western; Indian Ocean – eastern; Pacific – eastern central; Pacific – northwest; Pacific – western central
Range Map: Click here to open the map viewer and explore range.
Population [top]
Population: Abundance estimates on northern Queensland (Australia) reefs are 2.5–3.5 adults per 8000 m² (Choat in Pogonosky et al. 2002).
There are no data on total numbers of this fish globally. However, adults are largely limited to outer reef areas which are a small proportion of the total reef area within its distribution and, even in preferred habitats, densities are very low for a commercially exploited species (rarely > 10 fish per 10,000 square meter when not fished). It is considered uncommon to rare naturally. Nothing is known about the extent of subpopulations or degree of fragmentation but available suitable habitat is a major determinant of its distribution. Some edge of range extirpations are suspected.
The species is hermaphroditic, changing sex from female to male. The sex ratio of samples and fish observed in the field is female biased. Under IUCN criteria for mature individuals, there should be a correction made to factor in the sex bias which effectively reduces substantially the estimates of fish numbers included in this assessment.
Current Population Trend: Decreasing
Additional data:
Habitat and Ecology [top]
Habitat and Ecology: In one study, small post-settlement humphead wrasses were found in a species of seagrass (Enhalys acoroides), four species of hard coral (three Acropora spp. and Porites cylindricus), and in the soft coral Sarcophyton sp. (branching form; M.A. Tupper, pers. comm.). After settlement, juveniles and adults live associated with reef or near-reef habitats of seagrass beds and mangrove areas, with juveniles typically inshore and the largest individuals found in deeper waters of outer reefs or lagoons (Myers 1999). Juveniles of 3–20 cm TL, and larger, occur in coral-rich areas of lagoon reefs, particularly among live thickets of staghorn, Acropora spp. corals, in seagrass beds, murky outer river areas with patch reefs, shallow sandy areas adjacent to coral reef lagoons, and mangrove and seagrass areas inshore (Randall 1955, Randallet al. 1978, Myers 1999, J.H. Choat, pers. comm.). Recruitment patterns may vary considerably between years (M.A. Tupper, unpublished data). Adults are more common offshore than inshore, their presumed preferred habitat being steep outer reef slopes, reef drop-offs, reef tops, channel slopes, reef passes, and lagoon reefs to at least 100 m. They are usually found in association with well-developed coral reefs (Vivien 1973, Randall et all. 1978, Winterbottom et al. 1989, Allen and Swainston 1992, Sluka 2000). Typically they are solitary or paired, but have also been noted in groups of 3–7 individuals (Donaldson 1995). They appear to be somewhat sedentary in that the same individuals, indentifiable by distinct natural markings, may be seen along the same stretch of reef for extended periods. Indeed, many commercial dive sites have their ‘resident’ Humphead Wrasse, a favoured species for divers. Natural densities are evidently never high, even in presumed preferred habitats. For example, in unfished or lightly fished areas, densities may range from two to rarely more than 10–20 individuals per 10,000 m² of suitable reef. In fished areas, however, densities are typically lower by tenfold or more, and in some places fish no longer appear to be present.
Accounts of reproductive activity in the field reveal that, depending on location, this species spawns between several and all months of the year, in small or large groupings, that spawning coincides with certain phases of the tidal cycle, and that groups of spawning fish can form daily, at a range of different reef types. Spawning areas and aggregated adults have been noted regularly along specific sections of reef, sometimes associated with no obvious topographical features, sometimes close to the shelf edge on outer reefs, or adjacent to exposed reef passes near fairly steep drop-offs, or on mid-shelf (unspecified) reefs (P.L. Colin, J.H. Choat, R. Hamilton, S. Oakley, pers. comms.). The species is evidently a daily spawner that probably does not migrate far to its spawning site(s), spawning for extended periods each year, i.e., a ‘resident’ spawner (Domeier and Colin 1997, P.L. Colin, pers. comm.): groups of up to 150 fish were observed in Palau along the shelf edge in a loose aggregation.
Probable spawning aggregations have also been noted on Australia’s Great Barrier Reef (GBR), Fiji, New Caledonia, and in the Solomon Islands. Although spawning was not always observed, aggregated fish were ripe, or exhibiting behaviour likely associated with spawning. On the GBR, aggregations of up to 10 large males and 20–50 smaller fish (35–95 cm TL) were noted (J.H. Choat, pers. comm.). GBR aggregations from the Ribbon Reefs and north of Jewell Reef, once noted to include hundreds of fish, are no longer known at the same sites (Johannes and Squire 1988, L. Squire, pers. comm.).
The longevity of this species is up to at least 32 years, with females outliving the males (the oldest female recorded was 32 years), and sexual maturity is reached at about eight years of age (Choat in Pogonosky et al. 2002). Histological studies show that sexual maturation is reached at a size of between 40 cm and 60 cm total length (Sadovy, unpublished data). This species is thought to be a protogynous hermaphrodite, with sex reversal occurring at about 15 years of age (Choat in Pogonosky et al. 2002). At a total length of approximately 111 cm (Lau and Li 2000). Males grow very rapidly (Choat in Pogonosky et al. 2002).
It feeds on a variety of molluscs, fishes, sea urchins, crustaceans and other invertebrates (Randall et al. 1997).
Systems: Marine
Threats [top]
Major Threat(s): Threats include:
1) Intensive and species-specific removal for the live reef food fish export trade of a naturally uncommon and vulnerable species;
2) Readily accessible to spearfishing at night with SCUBA or hookah (i.e., compressed air) gear, and easy to catch with cyanide, or other poisons such as Derris trifoliata, due to predictable adult habitat and shallow depth range;
3) Lack of coordinated, consistent national and regional management largely due to limited management capacity and the sometime secretive nature of traders – in particular there is no relevant regional fishery management authority to address problems with this species;
4) Selective fishing, in particular the intensive take of juveniles for direct export sale and for grow-out (also referred to as ‘culture’ – the species cannot be hatchery reared; and
5) Illegal, unregulated, or unreported (IUU) fisheries (Donaldson and Sadovy 2001).
In addition, the species’ essential coral reef habitat is seriously threatened by human activity throughout the Indo-Pacific region. Destructive fishing practices, such as sodium cyanide use which stuns animals for capture and incidentally kills living coral, have been well documented and are spreading in the Indo-Pacific region (Barber and Pratt 1998, Burke et al. 2002, Bryant et al. 1998, Johannes and Riepen 1995). Despite its prohibition in many countries (including major exporters such as the Philippines and Indonesia), cyanide is still the preferred method for capturing certain live reef fish for international trade in some areas (Burke et al. 2002, Bryant et al. 1998, Johannes and Riepen 1995, Barber and Pratt 1998). Indeed, larger Humphead Wrasse are difficult to catch any other way, other than by night-time capture. When cyanide is applied, the fish often retreats into a crevice and becomes increasingly lethargic as the toxin reduces its ability to take up oxygen. Divers may break away the living coral to get access to the hiding area, and remove the fish to clean water where it will often recover for shipment or holding in net pens.
The most serious threat to this species is overfishing for the live fish export trade. They are mainly taken live for food – only rarely for the aquarium trade as far as can be determined. This species is long-lived and naturally uncommon, and if it is similar to other reef fishes of similar size and biology (e.g., sequential hermaphroditism; aggregation-spawner) it is expected to have low rates of replacement and therefore be particularly vulnerable to fishing pressure (Donaldson and Sadovy 2001). Moreover, being one of the largest of all reef fishes, they have few natural predators which means that fishing mortality may rapidly exceed natural mortality, possibly accounting for the rapid declines noted once fishing intensifies.
Although data are not available from throughout its range, wherever there are significant exports and no effective controls, fish numbers have declined substantially within a decade or less and exploitation rates are expected to continue, or more likely, intensify. There are few refuges for this species since live reef fish carriers have access to all reefs where it occurs and it does not extend into very deep water, probably little more than 60 m. Adults only occur in reasonable numbers where the fishery is effectively managed or where they occur in marine protected areas.
There has been speculation that Humphead Wrasse, and other reef fishes, can be cultured or "farmed" to meet international demand. However, it appears that the use of cultured fish may actually pose a threat to wild populations in certain circumstances since it does not involve hatchery production (not yet possible for this species and unlikely to be possible at commercial levels for many years according to experienced aquarist M.A. Rimmer, pers. comm.) but the grow-out of wild sourced juveniles.
Conservation Actions [top]
Conservation Actions: Australia
Western Australia – complete protection since May 1998 because stocks determined to be insufficient and susceptible to overfishing. From December 1st, 2003, Coral Reef Fin Fish Management Plan (for Queensland waters, including the Great Barrier Reef Marine Park) prohibited all take and possession of Humphead Wrasse, other than for limited educational purposes and public display.
China
Permits are required for the sale of this species in Guangzhou province, southern mainland China – for conservation purposes.
Indonesia
Fishing permitted if:
- Done by researcher (with research permit) for the purpose of scientific and mariculture development, as well as by artisanal fishers (with specific fishing permit).
- Allowable weights are 1 to 3 kg. Fish with weight less than 1 kg and more than 3 kg should be used for mariculture and/or freed to nature.
- Allowable fishing methods for catching humphead wrasse are hook and line, fish trap and gill net.
- With regards to artisanal fishers involve in fisheries business partnership, the fishers should sell the fish to its collector partners.
- Collector and exporters should develop a rearing and culturing facility in the collection site which is equipped with staff knowledgeable in reef fish culture.
- Provincial Fisheries Services much monitor, control and report on permits and volumes 3-monthly but no data were available despite multiple queries and are apparently not collected.
Maldives
All exports ofumphead Wrasse were banned in 1995, largely due to concern for recreational diving, a sector that values this species.
Niue
The interference, take, kill, or bringing to shore of the Humphead Wrasse is prohibited without written approval.
Palau
Illegal to fish, buy or sell humphead wrasse < 64 cm TL. Illegal to export Humphead Wrasse irrespective of size.
Papua New Guinea
There is a 65 cm minimum size limit for exporting Humphead Wrasse but this does not prevent fishers from catching and holding smaller Humphead Wrasse in cages (culturing) until they attain 65 cm TL. All live fish operators are required to obtain licenses.
Philippines
Exports of all live fish are technically prohibited from throughout the Philippines but this part of the code is evidently not implemented. Until recently Humphead Wrasse could not be exported from Palawan with an exemption for the taking of small fish for mariculture. The Palawan regulation is pending reconsideration. There was much illegal movement of this species outside of Palawan for subsequent export.
This species is listed on CITES Appendix II.
Citation: Russell, B. (Grouper & Wrasse Specialist Group). 2004. Cheilinus undulatus. The IUCN Red List of Threatened Species 2004: e.T4592A11023949. http://dx.doi.org/10.2305/IUCN.UK.2004.RLTS.T4592A11023949.en. Downloaded on 23 March 2016.
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