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Holothuria leucospilota

Source:IUCN

Taxonomy



 

Taxonomy in detail

Scientific name


 
Authority


 
Synonyms


 
Common names


 
Taxonomic sources
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Identification Information
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Taxonomic notes


 

Assessment Information

IUCN Red List Category and Criteria
Least Concern ver 3.1
Assessment language
English
Year published
2013
Date assessed
2010-05-18 00:00:00 UTC

Assessment Information in detail

Previously published Red List assessments


 
Regional assessments
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Assessor(s)


 
Reviewer(s)


 
Contributor(s)
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Facilitator(s) / Compiler(s)
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Partner(s) / Institution(s)
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Authority / Authorities
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Justification

This species is widespread in the Indian and tropical Pacific, and is very common in some parts of its range. It is fished, but not intensively given its low commercial value. It is listed as Least Concern.

Geographic Range

Native
Extant (resident)
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Extant
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Number of locations
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Geographic Range in detail

FAO Fishing Areas
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Estimated area of occupancy (AOO) (km²)
Continuing decline in area of occupancy (AOO)
Extreme fluctuations in area of occupancy (AOO)
Estimated extent of occurrence (EOO) (km2)
Continuing decline in extent of occurrence (EOO)
Extreme fluctuations in extent of occurrence (EOO)
Continuing decline in number of locations
Extreme fluctuations in the number of locationsN
RANGE DESCRIPTION
This species is widespread throughout the Indo-Pacific and Red Sea and Persian from South Africa to India, China to Australia, Hawaii, Polynesia, and east to Central America from Mexico to Peru.

Population

Current population trend
Unknown
Number of mature individuals
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Population severely fragmented
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Continuing decline of mature individuals
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Population in detail

Extreme fluctuations
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No. of subpopulations
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Continuing decline in subpopulations
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Extreme fluctuations in subpopulations
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All individuals in one subpopulation
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No. of individuals in largest subpopulation
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Description

This is the most frequently encountered and abundant Holothuria spp, after Holothuria atra in the Indian Ocean. The common name is the white thread fish.

In Malaysia, this is among the most abundant species (Choo 2008). In Vietnam, there was overexploitation of sea cucumbers; after the boom in catches in the late 1980s the average catch per diver of this species dropped. Before 1997, there were catches of many hundreds of tonnes per year of this species, and after 1997 it decreased to less than 100kg (Choo 2008). In La Réunion, it is one of the dominant species (Conand 2008), present in all sampling stations with total mean densities of 0.59 ± 0.38ind*m-2. Highest densities were in back reefs (mean 0.84 ± 0.38ind*m-2 versus 0.39 ± 0.26ind*m-2 in inner reef flats), with a maximum density of 1.4 ± 0.7ind*m-2 in Planch-Alizés station (Conand and Frouin 2007).

Bonham and Held (1963) estimated the total number of individuals of this species at Rongelap Atoll, Marshall Islands to be about 200,000 around peripheries of the larger islets and some reef and lagoon areas.

In Thailand, populations of this species have decreased in fishing areas (Bruckner et al. 2003).

Mean population density can exceed 0.5ind*m-1. Inshore, shallow water populations are denser, and composed of smaller individuals (Palomares and Pauly 2009).

Habitat and Ecology

System
Marine
Number of mature individuals
-
Continuing decline in area, extent and/or quality of habitat
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Generation length (years)
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Congregatory
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Movement patterns
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Habitat and Ecology in detail

Habitat and Ecology
In the Western Central Pacific, this species can be found over rubble, consolidated rubble and boulders between 0 and 5m (Kinch et al. 2008). In Malaysia, it prefers dead corals, in the shoreward side of the reef in depths up to 10m (Choo 2008). In the Africa and Indian Ocean, it prefers the back reef and reef flats over sand and rubble between 0 and 10m (Conand 2008). In Madagascar, it can be found in the inner slope, seagrass, microatoll and detrital fringe with higher densities in the inner slopes (Conand 2008). In Kenya, it hides under live coral heads in most coral reef habitats and at the fringes of seagrass beds (Muthiga et al. 2007). In China, this species lives in shallow waters up to 15m (Li 2004). In the Comores, it typically inhabits the calm and shallow zones over sandy bottoms or over coral rubble (Samyn et al. 2006).

It is often found in the intertidal area of the seaward sides of the islets at the edge of the reef-flat nearest shore (Marshall Islands). It can occupy pools of water from a few centimeters to about one half meter deep at low tide, and is occasionally entirely exposed (Bonham and Held 1963).

This species is a host to the pearl fish Encheliophis vermicularis (Eeckhaut 2004).

In the Great Barrier Reef (Australia), this species  reproduces between November and March whilst in the Northern Territory (Australia) it does so in April. In the Cook Islands, the information available states that this species reproduces from January to April and in November and December, or from October to January (Kinch et al. 2008). In Taiwan Province of China, this species reproduces between June and September (Choo 2008). In La Réunion, it reproduces twice a year, the first one in February and the second one in May. It reaches SOM at 180g (Conand 2008).

Classification scheme
Habitats Suitability Major importance

Threats

Use trade

This species is fished in many parts of its range, but has a very low value.

In the Western Pacific Region, this species is commercially exploited in Guam, FSM, Marshall Islands, Kiribati, Samoa, Tonga, Cook Islands, PNG, Solomon Islands and Fiji where it is consumed either whole or their intestines and/or gonads as delicacies or as protein in traditional diets; local consumption is of greater importance in times of hardship (i.e. following cyclones). In Southern Cook Islands, this species is exploited for their gonads by women and children all year long with special emphasis in the summer months. The removal of the organs does not seem to affect the general well being of the animal, with the wound healing afterwards. It is used in a subsistence fishery in Samoa, Cook Islands and Tonga (Kinch et al. 2008). In Asia, it is fished in China, Malaysia, Thailand, Indonesia, Philippines and Vietnam. In countries of South East Asia, this species is known to be part of the "worm" sea cucumbers, lower value, higher volume species (Choo 2008). It is fished in Madagascar (Rasolofonirina 2007), and China (Chen 2004, Li 2004).

This species is subjected for a fishery to satisfy the aquarium trade, with animals being collected in the Solomon Islands and some probably also from the Cook Islands, Fiji, French Polynesia, Tonga and Kiribati (Kinch et al. 2008).

Residential & commercial development
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Agriculture & aquaculture
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Energy production & mining
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Transportation & service corridors
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Biological resource use
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Human intrusions & disturbance
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Natural system modifications
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Pollution
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Geological events
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Climate change & severe weather
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Threats in detail

Threats
Although not one of the most important species (low value) for fishery purposes, it can be expected that this species may become more popular after the depletion or reduction of other species of higher commercial importance and value. As seen in Thailand after the decline of H. scabra (Choo 2008).
Classification scheme Threats
title scope timing score severity

Use trade

Use trade

This species is fished in many parts of its range, but has a very low value.

In the Western Pacific Region, this species is commercially exploited in Guam, FSM, Marshall Islands, Kiribati, Samoa, Tonga, Cook Islands, PNG, Solomon Islands and Fiji where it is consumed either whole or their intestines and/or gonads as delicacies or as protein in traditional diets; local consumption is of greater importance in times of hardship (i.e. following cyclones). In Southern Cook Islands, this species is exploited for their gonads by women and children all year long with special emphasis in the summer months. The removal of the organs does not seem to affect the general well being of the animal, with the wound healing afterwards. It is used in a subsistence fishery in Samoa, Cook Islands and Tonga (Kinch et al. 2008). In Asia, it is fished in China, Malaysia, Thailand, Indonesia, Philippines and Vietnam. In countries of South East Asia, this species is known to be part of the "worm" sea cucumbers, lower value, higher volume species (Choo 2008). It is fished in Madagascar (Rasolofonirina 2007), and China (Chen 2004, Li 2004).

This species is subjected for a fishery to satisfy the aquarium trade, with animals being collected in the Solomon Islands and some probably also from the Cook Islands, Fiji, French Polynesia, Tonga and Kiribati (Kinch et al. 2008).

Text summary


Text summary in detail

Conservation Actions Information
There are no known species specific conservation measures for this species. However, it may be present in some marine protected areas within its range.
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