Mountainous Star Coral
Mountainous Star Coral
Mountainous Star Coral
Mountainous Star Coral
Mountainous Star Coral
Invertebrate · Stinging · Hard corals

Mountainous Star Coral

Orbicella faveolata (Ellis & Solander, 1786)
syn. Madrepora faveolata, Montastraea faveolata, Montastrea faveolata
1-40 mCITES IIEndangered
1277

Orbicella faveolata, commonly known as mountainous star coral, is a colonial stony coral in the family Merulinidae. This coral is native to the coral coast of the 🌊 Caribbean Sea and the 🌊 Gulf of Mexico and has been classified as "endangered" by the International Union for Conservation of Nature. Previously known as Montastraea faveolata, it forms large, solid colonies that take the shape of mounds with a skirt. The surface of the coral is smooth and undulating, featuring small lumps, bulges, or lobes. The entire surface is covered in corallites, which are stony cups that serve as home to the polyps. These corallites have a diameter of about 5 mm (0.2 in). The typical coloration of Orbicella faveolata ranges from pale brown to yellowish green and grey, but it can also be deep brown with fluorescent green highlights. This coral is part of a species complex that includes closely related species like Orbicella annularis and Orbicella franksi, although the former displays more distinct nodules or small columns, and the latter has a more irregular and lumpy surface.

Orbicella faveolata can be found in shallow waters throughout its range in the 🌊 Caribbean Sea and the 🌊 Gulf of Mexico, including locations such as 🇺🇸 Florida, the 🇺🇸 United States, the 🇧🇸 Bahamas, 🇻🇪 Venezuela, and possibly 🇧🇲 Bermuda. It is commonly found on both the back reef and fore reef slopes of fringing reefs, typically at depths of up to 40 m (131 ft). In fact, it often dominates the fore reef slopes between depths of 10 and 20 m (33 and 66 ft).

Similar to other corals, Orbicella faveolata maintains a symbiotic relationship with dinoflagellates in the genus Symbiodinium, commonly referred to as zooxanthellae. These organisms are abundant in the coral's living tissue. The specific species of Symbiodinium associated with the coral depends on the intensity of light reaching particular regions on the coral's surface. If artificial shading is applied to corals, the Symbiodinium that reside in the shaded areas die off. However, when light is restored, zooxanthellae are reintroduced. In many cases, a different species of Symbiodinium replaces the original species. The surface of the coral can be considered a microbiome, a community of microorganisms. The composition of zooxanthellae, bacteria, and archaea present on the coral surface varies throughout the year. Additionally, the health of the coral and the presence of yellow-band disease can also influence the microbial composition, particularly during the spring season.

Orbicella faveolata is closely related to other coral species such as lobed star coral (Orbicella annularis) and boulder star coral (Orbicella franksi), which are also found in the 🌊 Caribbean Sea and the 🌊 Gulf of Mexico, including regions like the 🇧🇸 Bahamas and 🇧🇲 Bermuda. The species Paramontastraea saleborsa and Astrea curta have similar-sized corallites and share a taxonomic history with Orbicella faveolata, having also been placed in the coral genus Montastraea.

Due to its slow growth rate, the formation of new colonies is outpaced by the rate at which mature colonies perish. Orbicella faveolata is vulnerable to bleaching as well as several coral diseases, including yellow-band disease, black band disease, and plague. Over the past thirty years, population numbers have declined by more than 50%, leading to its classification as an "endangered" species by the International Union for Conservation of Nature.

Why it's threatened

Residential & commercial development
Housing & urban areas · Commercial & industrial areas · Tourism & recreation areas
Transportation & service corridors
Shipping lanes
Biological resource use
Intentional use: (subsistence/small scale) [harvest] · Unintentional effects: (subsistence/small scale) [harvest] · Motivation Unknown/Unrecorded
Human intrusions & disturbance
Recreational activities
Invasive species, genes & disease
Unspecified species · Named species · Diseases of unknown cause
Pollution
Type Unknown/Unrecorded · Soil erosion, sedimentation · Ozone
Climate change & severe weather
Temperature extremes · Storms & flooding

In general, the major threat to corals is global climate change, in particular, (i) temperature extremes leading to bleaching and increased susceptibility to disease, (ii) severity of ENSO events and storms, and (iii) ocean acidification. The most recent, and first, multi-year global bleaching event (spanning hundreds of kilometres or more) was from 2014 to 2017. Nearly 30% of reefs suffered mortality level-stress, more than 50% of affected reef areas were impacted at least twice, and some locations experienced almost complete coral cover loss (Blunden et al. 2018, Vargas-Angel et al. 2019, Eakin et al. 2019). The average interval between bleaching events is now more than 50% less than before, preventing full reef recovery (Hughes et al. 2018). Bleaching events influence the probability of coral spawning for several years. Corals that recover from bleaching events can experience long-term reduction in reproduction, over time scales that can bridge the interval between subsequent bleaching events (Levitan et al. 2014).

Coral disease has also emerged as a serious threat to coral reefs worldwide and is a major cause of reef deterioration (Weil et al. 2006, Richards et al. 2008, Maynard et al. 2015). As noted in Walton et al. (2018), in addition to thermal stress, increased coral disease prevalence and mortality can be linked to reduced water quality (Bruno et al. 2003) and clarity (van Woesik and McCaffrey 2017), nutrient enrichment (Vega Thurber et al. 2013), dredging associated sedimentation (Pollock et al. 2014, Miller et al. 2016), and plastic pollution. Based on a survey of 159 reefs in the Asia-Pacific region, the likelihood of disease increases 20-fold when corals are in contact with plastic (Lamb et al. 2018). Increased coral disease levels on the Great Barrier Reef were correlated with increased ocean temperatures (Boyett et al. 2007) supporting the prediction that disease levels will be increasing with higher sea surface temperatures.

In 2014, an outbreak of a coral disease termed Stony Coral Tissue Loss Disease (SCTLD) was reported off the coast of Miami-Dade County and has since spread along Florida and to some reefs in the Caribbean. At least 44% of Florida’s reef-building corals have been affected (Florida Department of Environmental Protection 2019). The pathogen causing the disease is unknown. This species is susceptible to SCTLD, with reported colony prevalence ranging from 5% to 63% in Florida during 2015-2018 (Precht et al. 2016, Combs 2019, Gintert et al. 2019), from 15 to 18% in the Mexican Caribbean in surveys conducted in 101 sites along 450 km from 2018 to 2020 (Alvarez- Filip et al. 2019, L. Alvarez-Filip pers. comm. 2020), and 10% in the Bahamas in 2020 (Dahlgren 2020). Up to September 2020, however, there have been no reports of SCTLD epizootic events in Cuba, Nicaragua, Costa Rica, Venezuela, and the Dominican Republic (Roth et al. 2020). SCTLD currently represents one of the greatest threats to this species due to: (1) its rapid spread across individual colonies; (2) high mortality rate; (3) rapid spread between reefs; (4) high infection rate (Pratte and Richardson 2014, Dahlgren 2020); and (5) overall change of the coral-associated microbiota (Meyer et al. 2019). This species is also susceptible to Black Band, White Plague, Dark Spot, and Yellow Band diseases and to bleaching.

Localized threats to this species include fisheries, human development (industry, settlement, resort development, tourism, and transportation), changes in native species dynamics (competitors, predators, pathogens and parasites), invasive species (competitors, predators, pathogens and parasites), pollution from agriculture and industry, domestic pollution, sedimentation, marine debris, human recreation and tourism activities. Other threats include predation by Sparisoma viride (Stoplight Parrotfish), hurricane damage, and loss of habitat at the recruitment stage due to algal overgrowth and sedimentation, as well as localized impacts due to bioerosion by sponges (mainly Cliona sp.) and other organisms. Species in this genus are among the preferred coral species for the extraction of tissue-skeleton cores to study different aspects of their biology, such as growth rate, calcification, or the effect of diseases, or to study skeletal environmental proxies such as climate change, paleo-nutrient proxies, water quality, or diagenesis. The extraction of cores from this species can deleteriously affect the remaining as the lesion can enlarge due to predation, competition with other sessile organisms (i.e. algae, sponges, or tunicates), or by the effect of boring organisms or pathogens. Full regeneration of this type of lesion has been reported to be low (<5% of the tissue; Rodríguez-Martínez et al. 2016). The severity of these combined threats to the global population of each individual coral species is not known, however, more than 60% of the world’s reefs are immediately threatened by local pressures (http://www.wri.org/project/reefs-at-risk; Bridge et al. 2013).

Threat classification from the IUCN Red List.

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Last Update: June 21, 2026