Humphead wrasse

Humphead wrasse
Breeding male humphead wrasse in the Melbourne Aquarium
Scientific classification
Kingdom: Animalia
Phylum: Chordata
Class: Actinopterygii
Order: Perciformes
Family: Labridae
Genus: Cheilinus
Species: C. undulatus
Binomial name
Cheilinus undulatus
Rüppell, 1835
Synonyms
  • Cheilinus mertensii Valenciennes, 1840
  • Cheilinus godeffroyi Günther, 1872
  • Cheilinus rostratus Cartier, 1874

The humphead wrasse (Cheilinus undulatus) is a species of wrasse mainly found on coral reefs in the Indo-Pacific region. It is also known as the Māori wrasse, Napoleon wrasse, Napoleon fish, Napoleonfish, so mei 蘇眉 (Cantonese), mameng (Filipino), and merer in the Pohnpeian language of the Caroline Islands.

Habitat

The humphead wrasses can be located with in the east coast of Africa and Red Sea, as well as in the Indian Ocean to the Pacific Ocean. Juvenile and adult humphead wrasses are found in different ranges. Juveniles are usually found in shallow, sandy ranges that are bordering coral reef waters, while adults are mostly found in offshore and deeper areas of the coral reefs, typically in outer-reef slopes and channels, but can also be found in lagoons. Humphead wrasses are found in small groups or larger combinations within their habitat.[2][3]

Description

The humphead wrasse is the largest living member of the family Labridae. Males are typically larger than females and are capable of reaching lengths of up to 2 meters from tip to tail and weighing up to 180 kg, but the average length is generally a little less than 1 meter. Females rarely grow larger than one meter in length. This species of fish can be easily identified by its large size, thick lips, two black lines behind its eyes, and the hump that appears on the forehead of larger adults. The color of the humphead wrasse can vary between a dull blue-green to more vibrant shades of green and purplish-blue. This particular reef fish prefers to live singly but adults are occasionally observed moving in small groups.[4][5][6]

Reproduction

The humphead wrasse is long-lived, but has a very slow breeding rate. Individuals become sexually mature at four to six years, and females are known to live for around 50 years, whereas males live a slightly shorter 45 years. Humphead wrasses are protogynous hermaphrodites, with some members of the population becoming male at about 9 years old. The factors that control the timing of sex change are not yet known. Adults move to the down-current end of the reef and form local spawning aggregations (they concentrate to spawn) at certain times of the year.[7] Humphead wrasses likely do not travel very far for their spawning aggregations.[8]

The humphead wrasse pelagic eggs and larvae ultimately settle on or near coral reef habitats. Eggs are 0.65 mm in diameter and spherical, with no pigment.[7]

Ecology

Napoleon fish diving in the Red Sea

Being very opportunistic predators, C. undulatus preys primarily on invertebrates such as mollusks (particularly gastropods and pelecypods), echinoids, crustaceans, annelids) and vertebrates, in the form of fish. Half of echinoids and most pelecypods hide under the sand, leaving one of two options: the humphead wrasses rely on fish excavators like stingrays, or they themselves excavate by ejecting water and nosing around to look for prey. Often, these wrasses, alone with many other Red Sea wrasses, crack sea urchins (echinoids) by carrying them to a rock in their mouths and striking them against a rock by moving their heads in sideways, brisk movements.[9]

Ocean acidification is becoming a threat to coral reefs because it is reducing the calcification rate of coral species. Due to an increased concentration of atmospheric CO2, the pH of Earth’s oceans are causing this acidification, and therefore decline in reef building activity. Adults are commonly found on steep coral reef slopes, channel slopes, and lagoon reefs in water 3 to 330 ft (1–100 m) deep. This species actively selects branching hard and soft corals and seagrasses at settlement. Juveniles tend to prefer a more cryptic existence in areas of dense branching corals, bushy macroalgae, or seagrasses, while larger individuals and adults prefer to occupy limited home ranges in more open habitat on the edges of reefs, channels, and reef passes. The species is most often observed in solitary male-female pairs, or groups of two to seven individuals.[10]

Conservation

A humphead wrasse at the water's surface on the Great Barrier Reef

The fish is listed as endangered on the IUCN Red list and in Appendix II of CITES.[11] Species numbers for the humphead wrasse have been declining due to a number of threats, including:

  1. Intensive and species-specific removal in the live reef food fish trade throughout its core range in Southeast Asia
  2. Destructive fishing techniques, including bombs and cyanide
  3. Habitat loss and degradation
  4. Local consumption and its value as a delicacy for local and tourists
  5. A developing export market for juvenile humphead wrasse for the marine aquarium trade
  6. Lack of coordinated, consistent national and regional management
  7. Inadequate knowledge about the species
  8. Illegal, unregulated, and unreported fishing activities[12]

As noted, one of the causes for population decline is the unsustainable and severe overfishing within the live reef food fish trade (LRFFT). Sabah (located on Borneo Island) is a major source for humphead wrasses. The fishing industry is specifically important to this state because of its severe poverty rates. The export of this fish out of Sabah has led to a roughly 99% decline in the population in that area. In an effort to protect the species there was a ban placed on the export of the humphead wrasse out of Sabah. However, this does not prevent illegal, unreported, and unregulated activities (IUU). The protection by the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) is managed in this area by the federal Department of Fisheries Malaysia, Sabah (DOFS) who issue permits to regulate fishing activity. There are two pieces of legislation that serve to protect the species as well. The Fisheries Act 1985 controls the transport of live fish as well as prohibits destructive fishing techniques and the Trade of Endangered Species Act 2008 supports Malaysia’s adoption of CITES.[12]

The humphead wrasse is considered to be an umbrella species, which means many other species are sympatric with this species and have much smaller ranges. The conservation of the habitat of an umbrella species such as the humphead wrasse would not only benefit this species, but also all of the other sympatric species. The concept of an umbrella species can lead to a better understanding of endangered species protection.[13]

The species has historically been fished commercially in northern Australia, but has been protected in Queensland since 2003 and Western Australia since 1998.

In Guangdong Province, southern mainland China, permits are required for the sale of this species; Indonesia allows fishing only for research, mariculture, and licensed artisanal fishing; the Maldives instituted an export ban in 1995; Papua New Guinea prohibits export of fish over 2 ft (65 cm) total length; and Niue has banned all fishing for this species.

The humphead wrasse is a U.S. National Marine Fisheries Service species of concern. Species of concern are those species about which the NMFS, has some concerns regarding status and threats, but for which insufficient information is available to indicate a need to list the species under the Endangered Species Act.

Population conservation by genetics

In 1996, the humphead wrasse was listed as a vulnerable species in the IUCN Red List because in the last decade, humphead wrasse populations were declining rapidly. The genomes of the humphead wrasse must be evaluated so as to try to determine a way to help keep the species alive.[14]

Since so little is known about the genetic relationships at a geographical scale of the humphead wrasse, due to a test using microsatellite loci, (usually DNA markers are used for this specific test, but the humphead wrasses lack such markers,) researchers were able to facilitate population genetic studies in this species.

Of the 15 microsatellite loci used in the test, only four of them seem to have a different outcome than the other 11 loci. These microsatellite loci were all prone to null alleles. However, with the presence of these null alleles, the results may have been slightly biased, or they may be related to a particularity of the C. undulatus, which are highly restricted to coral reef habitats.[15]

Illegal, unregulated, and unreported activities

The Philippines, Indonesia, and Sabah Malaysia are the three largest exporters of the humphead wrasse. The fish has one of the highest retail values in Asia, especially if caught alive, and it is a delicacy in places like Malaysia. Illegal, unregulated, and unreported (IUU) activities were identified as the major factor contributing to the failure of conservation efforts. Although the Convention on International Trade in Endangered Species of Wild Fauna and Flora has placed a ban on the exportation of the humphead wrasse, in many cases, the fish are still being smuggled across the Malaysian–Philippine border.[12]

Four main factors have led to the persistence of IUU activities:

  1. Lack of capacity: A lack exists of formal procedures and the work force that monitor fishing activities and enforce fishing regulations.
  2. Lack of disincentives: Fishers do not have alternatives to substitute for the humphead wrasse, due to its value. Also, sanctions for illegal activities are not harsh enough to discourage fishing of this species.
  3. Weak accountability systems: A number of people are involved in the trade of this species, making it difficult to trace its source. Also, importers and consumers alike, despite their involvement, cannot be held responsible for the illegal exportation of the humphead wrasse.
  4. Absent domestic trade controls: Regulatory gaps are seen in that domestic catching, possession, and trading of the fish are not restricted fishers may illegally source the fish or have intentions to illegally trade it, but if they are within Malaysian waters and have appropriate permits, they cannot be prosecuted.[12]

The top exports of the humphead wrasse in Malaysia were in Sandakan, Papar, and Tawau. The fish could be purchased from between US$45.30 and $69.43, while the retail price ranged from $60.38 to $120.36.[16][17]

See also

References

  1. Russell, B. (Grouper & Wrasse Specialist Group) 2004. Cheilinus undulatus. In: IUCN 2013. IUCN Red List of Threatened Species. Version 2013.1. <www.iucnredlist.org Archived June 27, 2014, at the Wayback Machine.>. Downloaded on 02 November 2013.
  2. Sluka, Robert (November 2005). "Humphead Wrasse (Cheilinus Undulatus) Abundance and Size Structure Among Coral Reef Habitats in Maldives". Atoll Research Bulletin. 538: 192–198. doi:10.5479/si.00775630.538.189.
  3. Tupper, Mark (2007). "Identification of nursery habitats for commercially valuable humphead wrasse Cheilinus undulatus and large groupers (Pisces: Serranidae) in Palau". Marine Ecology Progress Series. 332: 189–199. doi:10.3354/meps332189.
  4. Chateau, Wantiez (2007). "Site fidelity and activity patterns of a humphead wrasse, Cheilinus undulatus (Labridae), as determined by acoustic telemetry". Environmental Biology of Fishes. Springer Netherlands. 80: 503–508. doi:10.1007/s10641-006-9149-6.
  5. Weng, Pederson, Del Raye, Caselle, Gray (2015). "Umbrella species in marine systems: using the endangered humphead wrasse to conserve coral reefs". Inter-Research Endangered Species Research.
  6. Sadovy, Kulbicki, Labrosse, Letourneur, Lokani, Donaldson (September 2003). "The Humphead Wrasse, Cheilinus undulatus: synopsis of a threatened and poorly known giant coral reef fish" (PDF). Reviews in Fish Biology and Fisheries. 13: 327–364. doi:10.1023/B:RFBF.0000033122.90679.97.
  7. 1 2 Sadovy, Y et. al. (2003). "Synopsis of a Threatened and Poorly Known Giant Coral Reef Fish". Fish Biology and Fisheries. 13 (3): 327–364. doi:10.1023/b:rfbf.0000033122.90679.97.
  8. Chateau, Olivier; Lantiez, Laurent (2007). "Site fidelity and activity patterns of a Humphead wrasse, Cheilinus undulatus (Labridae), as determined by acoustic telemetry". Environmental Biology of Fishes. 80 (4): 503–508. doi:10.1007/s10641-006-9149-6.
  9. Randall, J.E et. al. (1978). "Food habits of the giant humphead wrasse, Cheilinus undulatus (Labridae)" (PDF). Environmental Biology of Fishes. 3: 235–238. doi:10.1007/bf00691948.
  10. Tupper, Mark (2007-03-05). "Identification of nursery habitats for commercially valuable humphead wrasse Cheilinus undulatus and large groupers (Pisces: Serranidae) in Palau". Marine Ecology Progress Series. 332: 189–199. doi:10.3354/meps332189.
  11. Dorenbosch. et. al., M (2006). "Seagrass beds and mangroves as potential nurseries for the threatened Indo-Pacific humphead wrasse, Cheilinus undulatusand Caribbean rainbow parrotfish, Scarus guacamaia" (PDF). Biological Conservation. 129: 277–282. doi:10.1016/j.biocon.2005.10.032.
  12. 1 2 3 4 Poh, T. (2012). "Tackling illegal, unregulated, and unreported trade towards Humphead wrasse (Cheilinus undulatus) recovery in Sabah, Malaysia". Marine Policy. 36 (3): 696–702. doi:10.1016/j.marpol.2011.10.011.
  13. Weng, K. C et. al. (2015). "Umbrella species in marine systems: using the endangered humpback wrasse to conserve coral reefs". Endangered Species Research. 27: 251–263. doi:10.3354/esr00663.
  14. Qi, X. Z et. al. (2013). “Complete mitochondrial genome sequence of the humphead wrasse, Cheilinus undulates”. <http://www.funpecrp.com.br/gmr/year2013/vol12-2/pdf/gmr2248.pdf>
  15. Hu, J et. al. (2013). “Development and characterization of microsatellite loci in a threatened marine fish, Cheilinus undulatus (humphead wrasse)” <http://www.funpecrp.com.br/gmr/year2013/vol12-3/pdf/gmr2433.pdf>
  16. Chen, J.N.S; Justin, S.R. (2009). "Regulating the humphead wrasse (cheilinus undulatus) trade in Sabah, Malaysia". Ambio.
  17. Fenner, Douglas (2014-07-15). "Fishing down the largest coral reef fish species". Marine Pollution Bulletin. 84 (1–2): 9–16. doi:10.1016/j.marpolbul.2014.04.049.
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