Napoleon Wrasse
Napoleon Wrasse
Napoleon Wrasse
Napoleon Wrasse
Poisonous
Fishes · Bony fishes · Wrasse

Napoleon Wrasse

Cheilinus undulatus Rüppell, 1835
syn. Cheilenus undulatus, Cheilinus godeffroyi, Cheilinus mertensii, Cheilinus rostratus, Cheilinus undulates, Chelinus godeffroyi +5 more
2 m180 kg1-100 mCITES IIPoisonousEndangered
2900

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

As the largest living member of the labridae family, male humphead wrasses can reach impressive sizes, measuring up to 2 meters in length and weighing up to 180 kg. However, the average length for this species is slightly less than 1 meter. Females, on the other hand, rarely grow larger than one meter. Distinguishing characteristics of the humphead wrasse include its substantial size, thick lips, two black lines behind its eyes, and the prominent hump on the foreheads of larger adults. The coloration of this species can vary, ranging from dull blue-green to more vibrant shades of green and purplish-blue. While adults are often observed living alone, they can also be found in male/female pairs or small groups.

The humphead wrasse inhabits various regions, including the east coast of Africa around the 🌊 Red Sea, as well as certain areas of the 🇮🇳 Indian and 🌊 Pacific Oceans. Juveniles prefer shallow, sandy ranges adjacent to coral reef waters, while adults predominantly reside in offshore and deeper sections of coral reefs, typically on outer-reef slopes and channels, and sometimes within lagoons.

With a long lifespan and slow breeding rate, the humphead wrasse matures sexually between five to seven years of age and is known to live for approximately 30 years. They exhibit protogynous hermaphroditism, with some individuals transitioning to the male sex around nine years old. However, the precise factors governing sex change timing are not yet fully understood. These fish congregate in local spawning aggregations during certain times of the year, typically moving towards the down-current end of the reef. Their spawning aggregations likely occur relatively close to their usual habitats. The pelagic eggs and larvae eventually settle on or near coral reef environments. The eggs are spherical, measuring 0.65 mm in diameter and lacking pigmentation.

The humphead wrasse possesses an opportunistic predatory nature, primarily preying on invertebrates such as molluscs (particularly gastropods), pelecypods, echinoids, crustaceans, and annelids, as well as other fish, including poisonous sea urchins and crown-of-thorns starfish. Can be toxic. In their search for prey, they may rely on fish excavators like stingrays or adopt excavation techniques themselves by expelling water to displace sand and uncover potential prey. Similar to other wrasses in the 🌊 Red Sea, humphead wrasses have been observed cracking open sea urchins (echinoids) by carrying them in their mouths and striking them against rocks using brisk, sideways head movements. They sometimes engage in cooperative hunting with the roving coral grouper. Adults are commonly found in steep coral reef slopes, channel slopes, and lagoon reefs, typically at depths ranging from 1 to 100 meters (3 to 330 feet).

During the settlement phase, this species actively selects branching hard and soft corals, as well as seagrasses. Juvenile humphead wrasses tend to prefer cryptic habitats, residing in areas with dense branching corals, bushy macroalgae, or seagrass beds. In contrast, larger individuals and adults favor more open habitats on the periphery of reefs, channels, and reef passes, establishing limited home ranges.

Why it's threatened

Biological resource use
Intentional use: (subsistence/small scale) [harvest] · Intentional use: (large scale) [harvest]
Climate change & severe weather
Temperature extremes

This species is clearly conservation-dependent (Gillett 2010) and, while there are numerous threats to its persistence in the wild, the synergistic nature of intrinsic and extrinsic factors result in exploitation being its primary threat. Intrinsic factors such as naturally low densities and population size, longevity, hermaphroditic reproductive strategy, and night-time dormancy enhance the species’ vulnerability to exploitation. Extrinsic factors such as a lack of appropriate and enforced management actions (including Illegal, Unreported, and Unregulated [IUU] fishing) and unchecked harvest of juveniles for grow-out operations result in unsustainable fishing operations, while habitat loss is likely decreasing the ability of populations to recover even in areas where the species has enforced protection because of its close association with coral reef habitat, which is impacted by degradation processes related to climate change.

The susceptibility to overfishing is enhanced by several factors such as: (1) the bulk of the fishery for live fish export (the major trade in the species) is located in the southwest Philippines and Indonesia, two large areas where the species is not adequately managed for sustainability and that make up a large portion of the species' range and global population; (2) much of the export fishery is selective for juvenile, “plate-sized” fish as these are the preferred size by consumers and gain high prices (the species is one of the two top-priced species in the live fish trade), making them highly profitable for traders; (3) uncontrolled and heavy fishing for juvenile fish of a range of sizes for grow-out (from just post-settlement to several years of age) has removed hundreds of thousands of individuals from Indonesia (over multiple years) (inferred from Mujiyanto et al. 2020, Arieta 2022) despite regulations to help safeguard the species, these are generally not well enforced and pressures for young for grow-out are set to continue or increase; (4) illegal international trade occurs especially on fish carrier vessels which are poorly controlled, e.g., between Indonesia and Hong Kong, Philippines and Malaysia and out of Malaysia and Philippines. Illegal cross-border trade also occurs between the southwest Philippines and Malaysia (Chen and Justin 2009, Poh and Fanning 2012, Wu and Sadovy de Mitcheson 2016, BFAR 2017, Kindsvater et al. 2017, Sadovy de Mitcheson et al. 2017, Hau and Sadovy de Mitcheson 2023); 5) indiscriminate capture in non-selective gears, notably gill nets, in small scale fisheries in developing countries in the Indian Ocean; 6) susceptibility of sleeping fish in coral crevices to selective spear fishery at night (Sadovy et al. 2003); and 7) uncontrolled domestic use remains a threat in some countries.

There is concern that the increased move to juvenile fisheries (taking juveniles of a range of sizes for grow-out in cages) is placing growing pressure on the species and is occurring in areas where few adults are recorded in underwater surveys. The legal trade in capture-based cultured fish was introduced in 2017 in Indonesia, the only legal exporter of the species under CITES, and as of 2024, all export trade is in fish caught for grow-out which have not been assessed (as required under CITES), for a sustainable export quota; grow-out fish are also illegally exported from the Philippines because the non-detriment find (NDF) does not support exports (Hau and Sadovy de Mitcheson 2023).

Threat classification from the IUCN Red List.

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Last Update: June 28, 2026