|Scientific Name:||Thalassoma cupido (Temminck & Schlegel, 1845)|
Julis cupido Temminck & Schlegel, 1845
|Red List Category & Criteria:||Least Concern ver 3.1|
|Assessor(s):||Shea, S., Liu, M. & Sadovy, Y.|
|Reviewer(s):||Craig, M.T. & Carpenter, K.E.|
This species is found in Tawian, Japan and Korea, and is likely abundant throughout its range. There are no known major threats to this species. It is listed as Least Concern.
|Range Description:||This species occurs in the northwest Pacific, including the Republic of Korea, Japan, and Taiwan.|
Native:Japan; Korea, Republic of; Taiwan, Province of China
|FAO Marine Fishing Areas:|
Pacific – northwest
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||There is no population information available for this species. It is likely abundant throughout its small range.|
It is one of the most common shore-fish in Igaya Bay, southern Japan (Moyer 1974).
|Current Population Trend:||Unknown|
|Habitat and Ecology:||This species occurs in coral and rocky areas from 3-10 m (R. Myers pers. comm. 2008). It has been observed in coral atolls (Nanami and Nishihira 2004). Juveniles feed on small crustaceans including copepods, isopods, tanaids and cumaceans from algal mats, while adults consume polychaetes, sipunculids, gastropods, chitons and crustaceans including crabs, shrimps and hermit crabs (Shibuno et al. 1993).|
It was reported to spawn during mid-morning, before 10:00 am (Moyer 1974, Meyer 1977), group or aggregate spawning (Meyer 1977) by the terminal phase was observed in the Japanese waters. There was no evidence of spawning during late morning and afternoon, and the observations of spawning were four days prior to the new moon (Moyer 1974). Breeding ground of this species is approximately 200 m2, varying from nine to 11 m in depth. Water temperature was 27 °C (Moyer 1974).
Spawning begins with the arrival of large numbers of initial-phase fish at the coral or rocky areas, where they begin to mill about in increasingly tighter aggregations (Thresher 1984). The size of aggregations varies from a dozen to as many as several hundred individuals with different-sized aggregates. In addition, it has been reported to perform a “bobbing” motion while swimming with the entire body arcing up and down (Moyer 1974, Meyer 1977).
Moyer (1974) described the spawning behaviour of T. cupido in detail. During the first day of spawning, this species aggregates close to the rocks, and split periodically into three or four groups of close to 100 individuals each. Larger fish appeared to be about 10-13 cm in length and were obviously the aggressors. Only one or rarely two or three fish in each group dash up to discharge their reproductive clouds. Second day, the number of fish participating had decreased remarkably compared to the first day. On the fifth day, reproductive activity has almost ceased, but small individuals of about fifteen fish were sighted. Little herding and no clouds of reproductive materials were observed.
Hatched in a captivity laboratory environment, eggs of this species were found to be buoyant and spherical with a single spherical oil globule. Diameters ranged from 0.54 mm to 0.65 mm and spawning was observed from June to August in the morning between 0800 to 1200 (Kimura et al. 1998).
It exhibits similar colour patterns with T. purpureum, T. trilobatum, T. quinquevittatum and T. heiseri (Bernardi et al. 2004). It has been reported to be a protogynous hermaphrodite (Devlin and Nagahama 2002), however, gonadal histology has not been studied in any detail (Sadovy de Mitcheson and Liu 2008). It has been noted as one of the cleaner fishes in Japan (Kuwamura 1976).
|Congregatory:||Congregatory (and dispersive)|
|Use and Trade:||This species is utilized as food and is also collected for the aquarium trade. In Taiwan, it is caught for food and for the aquarium trade (Shao 2008). In Japan, labrids are caught by both commercial and recreational fishing (Kimura et al. 1998), but there is no information on the catches of this species.|
|Major Threat(s):||There are no major threats known to this species, although it is caught in both recreational and commercial multi-species fisheries.|
There are no specific conservation measures in place for this species. Its distribution overlaps several marine protected areas within its range.
This species was recorded in the Saikai National Park, including Fukue and Wakamatsu Marine Parks, Japan (DINRAC 2007). However, most of the MPAs situated in southeast Asia are considered to be poorly managed and subjected to heavy illegal fishing pressure (Chou et al. 2002).
|Citation:||Shea, S., Liu, M. & Sadovy, Y. 2010. Thalassoma cupido. The IUCN Red List of Threatened Species 2010: e.T187446A8537893.Downloaded on 21 November 2017.|
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