Taxon name
Lethrinus nebulosus
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Lethrinus nebulosus
(Forsskål, 1775)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Species authority
(Forsskål, 1775)
Taxonomic notes and synonyms listed
Lethrinus nebulosus may represent a complex of species, and further taxonomic work is required (K. Carpenter pers. comm. 2015). A cryptic species under L. nebulosus was detected in a study off southeastern Africa, but further study is required to resolve the taxonomy and distribution (Healey et al. 2018).
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Qualifying criteria (if given)
A2bcd+4bcd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This inshore, reef-associated species occurs throughout UAE waters. It is heavily exploited in the UAE, and stock assessments conducted for Abu Dhabi in 2006, 2010 and 2018 reported it as overfished. Based on catch data and stock assessments, this species has undergone an inferred declined of at least 52-78% over the past two generation lengths, or 14 years. With recent fisheries management measures implemented in Abu Dhabi, it is difficult to say whether fishing effort will continue to increase or decrease within the near future. Considering that other Emirates and surrounding countries that likely share this stock do not have management measures in place to reduce effort in the gargoor fishery, population declines are expected to continue. In addition, degradation of coastal habitats in the UAE and Arabian Gulf region, especially for coral reefs, is expected to continue. The population in UAE is inferred to have some level of connectivity with those in surrounding countries, and declines have been reported from Saudi Arabia, Qatar and Kuwait. It is listed as Endangered A2bcd+A4bcd. In addition to improvements needed in fisheries management, taxonomic research is also recommended.
Assessment details
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. As is currently understood on the global-level, it is widespread in the Indo-West Pacific (Carpenter and Allen 1989). Its depth range is 0 to 90 m (R. Myers pers. comm. 2015).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Habitat
Habitat details as listed in assessment
This species inhabits nearshore and offshore coral reefs, coralline lagoons, seagrass beds, mangrove swamps, coastal sand and rock areas to depths of 75 m (Carpenter and Allen 1989). It is occasionally observed in small aggregations (Randall 1995), but adults typically occur singly. It primarily consumes molluscs, crustaceans, echinoderms and less often polychaetes and fishes (Carpenter and Allen 1989). The maximum total length is 87 cm (Assadi and Dehghani 1997). This species undergoes a protogynous sex change that occurs over a wide range of year groups starting with age 1, well before maturity (McPherson et al. 1985). Longevity is estimated to be 14-26 years (Mathews and Samuel 1991, Edwards and Shaher 1991, Dalzell et al. 1996, Grandcourt 2006, Ebisawa and Ozawa 2009). Off the Ryukyu Islands of Japan, the age of 50% ovarian maturity was 4 years (Ebisawa and Ozawa 2009). This species forms spawning aggregations (Salem 1999). In the southern Arabian Gulf, spawning occurs between April to May, the mean size and age at first sexual maturity for males and females to be 19.4 cm and 0.5 years for males and 28.9 cm and 2.7 years for females, and maximum age was 11 years (Grandcourt et al. 2006 and 2010). When applying an age at first reproduction of 3 years and longevity of 11 years, its estimated generation length is 7 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Threats and conservation measures listed
Threats listed in assessment
Overfishing is a major threat to this species in the Arabian Gulf. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.