Porites lutea | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Taxa
Porites lutea | Milne Edwards & Haime, 1851
Location
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Scope (Assessment)
National
Taxon
Taxonomic Group
Invertebrates
Taxonomic Group Level 2
Corals
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is reported from UAE waters in the Gulf and Sea of Oman (Riegl et al. 2012, R. Bento pers. obs. 2019).Elsewhere, this species is widely distributed in the Indo-Pacific.
Habitats and Ecology
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species occurs with P. lobata and P. australiensis on back reef margins, lagoons and fringing reefs, generally to depths of 30 m. It is commonly found from 1-15 m, with massive colonies at 3-5 m in the South China Sea and Gulf of Siam (Titlyanov and Titlyanova 2002). In American Samoa, one colony is known to be 6.5 m tall and 41 m circumference (D. Fenner pers. comm. 2008).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. Total longevity is not known, but likely to be more than ten years. Furthermore, based on average sizes and growth rates, we assume that average generation length is 10 years, unless otherwise stated. Therefore, any population decline rates for the Red List assessment are measured over at least 30 years.
Is there a map available in assessment?
Yes
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
A2bc
Assessment rationale/justification
This stony coral is common and likely found along both coasts of the UAE. It can survive sedimentation and has low susceptibility to bleaching, but other species of Porites are particularly susceptible to disease and harvesting for aquarium trade, and extensive reduction of coral reef habitat due to a combination of threats. Species-specific population trend data are not available and therefore are based on the data available for the genus. Despite the relatively low susceptibility to bleaching, the most recent bleaching event (2017) resulted in over 75% mortality of Porites in shallow-water habitats of Abu Dhabi. Elsewhere, however, Porites are in better shape. For example, Porites species are relatively stable in Dubai. In Fujairah, Porites species are increasing, likely recovering from an earlier decline after a massive harmful algal bloom and cyclone in 2007-2008. Although recent (post-2011) data are limited, there have been no major disturbances since then. As this species is more abundant in areas that are improving in status, it is suspected that overall declines in the UAE are likely approaching but not exceeding 30% over three generations (1989-2019). Therefore, it is listed as Near Threatened under criterion A2bc. No regional adjustment is made to the Near Threatened listing.
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
In the Gulf, the major threats to corals include extreme and increasing temperature variability due to climate change, as well as direct destruction and increased turbidity caused by coastal construction (Riegl et al. 2012). Although bleaching thresholds in the Gulf are the highest recorded in the world (Riegl et al. 2012), bleaching events in the UAE have resulted in significant mortality (such as in 1996-1998, 2002, 2010 and 2017) and slow recovery (Burt et al. 2008). In Abu Dhabi, the most recent coral bleaching event resulted in nearly 95% of corals bleaching, and by April 2018, mortality reached 73% (Burt et al. 2019). This event resulted in mass mortality of even the more stress-tolerant corals such as poritids and merulinids (Burt et al. 2019). Coastal development, particularly large-scale offshore real estate developments and sedimentation associated with reclamation, has directly buried coral reefs in the Gulf (Burt et al. 2008, 2013; Burt 2014; Burt and Bartholomew 2019). In the Sea of Oman, UAE reefs have experienced major hurricanes and harmful algal blooms that caused high coral mortality and shifted community structure (Bauman et al. 2010, Foster et al. 2011).The genus is not particularly susceptible to bleaching, but is more prone to disease than many other corals. Coral disease has emerged as a serious threat to coral reefs worldwide and is a major cause of reef deterioration (Weil 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 et al. 2006). Increased coral disease levels on the Great Barrier Reef were correlated with increased ocean temperatures (Willis et al. 2004) 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.Globally , 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. In addition to global climate change, corals are also threatened by a number of localized threats. 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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Scientific Name Kingdom Phylum Class Order Family Genus
Porites lutea Animalia Cnidaria Anthozoa Scleractinia Poritidae Porites