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Taxon ID: 33,102 Total records: 39,143

Lobophyllia serratus

Country

Country Brunei Darussalam
Continent Ocean Asia

Classification

Kingdom Animalia (COL)
Phylum Cnidaria (COL)
Class Anthozoa (COL)
Order Scleractinia (COL)
Family Mussidae (COL)

Taxonomy

Genus Lobophyllia Reference
SubGenus Vernacular Name
Species serratus IUCN Threat Status-Year Endangered, 2008
SubSpecies Nat'l Threat Status-Year Not Evaluated, 2000
Infraspecies Reason for Change
Infraspecies Rank CITES
Taxonomic Group Anthozoans Native Status Native
Scientific Name Author Veron, 2002 Country Distribution Brunei Darussalam
Citation Description Geographic Range [top] Range Description: This species is found in the central Indo-Pacific. Papua New Guinea (Fenner 2003). Countries occurrence: Native: Australia; Indonesia; Malaysia; Papua New Guinea; Philippines; Singapore; Thailand FAO Marine Fishing Areas: Native: Indian Ocean – eastern; Pacific – northwest; Pacific – western central Additional data: ? Lower depth limit (metres): 15 ? Upper depth limit (metres): 4 Range Map: Click here to open the map viewer and explore range. Population [top] Population: This species is rare. There is no species specific population information available for this species. However, there is evidence that overall coral reef habitat has declined, and this is used as a proxy for population decline for this species. This species is particularly susceptible to bleaching, disease, and other threats and therefore population decline is based on both the percentage of destroyed reefs and critical reefs that are likely to be destroyed within 20 years (Wilkinson 2004). We assume that most, if not all, mature individuals will be removed from a destroyed reef and that on average, the number of individuals on reefs are equal across its range and proportional to the percentage destroyed reefs. Reef losses throughout the species range have been estimated over three generations, two in the past and one projected into the future. The age of first maturity of most reef building corals is typically three to eight years (Wallace 1999) and therefore we assume that average age of mature individuals is greater than eight years. Furthermore, based on average sizes and growth rates, we assume that average generation length is 10 years, unless otherwise stated. Total longevity is not known, but likely to be more than ten years. Therefore any population decline rates for the Red List assessment are measured over at least 30 years. See the supplementary material for further details on population decline and generation length estimates. [Get Adobe Reader] For further information about this species, see Corals_SupportingDoc.pdf. A PDF viewer such as Adobe Reader is required. Current Population Trend: Unknown Additional data: ? Population severely fragmented: No Habitat and Ecology [top] Habitat and Ecology: This species is found on reef slopes. This species is found from 4-15 m. Systems: Marine Generation Length (years): 10 Threats [top] Major Threat(s): This species is likely collected for the aquarium trade under a different name. In general, the major threat to corals is global climate change, in particular, temperature extremes leading to bleaching and increased susceptibility to disease, increased severity of ENSO events and storms, and ocean acidification. Coral disease has emerged as a serious threat to coral reefs worldwide and a major cause of reef deterioration (Weil et al. 2006). The numbers of diseases and coral species affected, as well as the distribution of diseases have all increased dramatically within the last decade (Porter et al. 2001, Green and Bruckner 2000, Sutherland et al. 2004, Weil 2004). Coral disease epizootics have resulted in significant losses of coral cover and were implicated in the dramatic decline of acroporids in the Florida Keys (Aronson and Precht 2001, Porter et al. 2001, Patterson et al. 2002). In the Indo-Pacific, disease is also on the rise with disease outbreaks recently reported from the Great Barrier Reef (Willis et al. 2004), Marshall Islands (Jacobson 2006) and the northwestern Hawaiian Islands (Aeby 2006). Increased coral disease levels on the GBR were correlated with increased ocean temperatures (Willis et al. 2007) supporting the prediction that disease levels will be increasing with higher sea surface temperatures. Escalating anthropogenic stressors combined with the threats associated with global climate change of increases in coral disease, frequency and duration of coral bleaching and ocean acidification place coral reefs in the Indo-Pacific at high risk of collapse. Localized threats to corals include fisheries, human development (industry, settlement, tourism, and transportation), changes in native species dynamics (competitors, predators, pathogens and parasites), invasive species (competitors, predators, pathogens and parasites), dynamite fishing, chemical fishing, pollution from agriculture and industry, domestic pollution, sedimentation, and human recreation and tourism activities. The severity of these combined threats to the global population of each individual species is not known. Conservation Actions [top] Conservation Actions: All corals are listed on CITES Appendix II. Parts of the species’ range fall within Marine Protected Areas. Recommended measures for conserving this species include research in taxonomy, population, abundance and trends, ecology and habitat status, threats and resilience to threats, restoration action; identification, establishment and management of new protected areas; expansion of protected areas; recovery management; and disease, pathogen and parasite management. Artificial propagation and techniques such as cryo-preservation of gametes may become important for conserving coral biodiversity. Having timely access to national-level trade data for CITES analysis reports would be valuable for monitoring trends this species. The species is targeted by collectors for the aquarium trade and fisheries management is required for the species, e.g., MPAs, quotas, size limits, etc. Consideration of the suitability of species for aquaria should also be included as part of fisheries management, and population surveys should be carried out to monitor the effects of harvesting. Recommended conservation measures include population surveys to monitor the effects of collecting for the aquarium trade, especially in Indonesia. Citation: Turak, E., Sheppard, C. & Wood, E. 2008. Lobophyllia serratus. The IUCN Red List of Threatened Species 2008: e.T133226A3641250. http://dx.doi.org/10.2305/IUCN.UK.2008.RLTS.T133226A3641250.en. Downloaded on 04 June 2018. Disclaimer: To make use of this information, please check the . Feedback: If you see any errors or have any questions or suggestions on what is shown on this page, please provide us with feedback so that we can correct or extend the information provided
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Synonyms


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Common Names


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Localities


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Species Record Updated By: Carlos Aurelio Callangan