Coral diseases are transmissible pathogens that cause the degradation of coral colonies. Coral cover in reef ecosystems has decreased significantly for a diverse set of reasons, ranging from variable environmental conditions to mechanical breakdowns from storms. [1] [2] In recent years, diseases that infect and kill coral have shown to be a threat to the health of coral reefs. Since the first coral disease was reported in 1965, many different kinds of diseases have popped up in mostly Caribbean waters. [3] These diseases are diverse, including pathogens of bacteria, fungi, viruses, and protozoans. [1] Coral diseases have widespread implications, impacting entire ecosystems and communities of organisms. Researchers are working to understand these diseases, and how potential treatments could stop these pathogens from causing the widespread death of corals in a way that permanently impacts the community structure of reefs. [4] [5]
Like other organisms, stony corals and soft corals are subject to disease. This may not have been obvious in the past, but is becoming increasingly apparent in the twenty-first century. The rising ill health of corals is partially the result of the corals being subjected to increasing amounts of stress as the physical environment around them becomes less suited to their needs. [1] [2] Corals live within a precise range of abiotic environmental conditions including water temperature, salinity and water quality. Variations outside the normal range of these parameters may make the corals less able to grow and reproduce successfully, and may make them more susceptible to diseases. [1] One of the major consequences that can occur with stress is the coral expelling its zooxanthellae, which are mutualistic algae that live inside coral. Corals without their symbionts become bleached, which effectively kills them since they are unable to gain the correct nutrients without their symbionts. Corals being sensitive to stress factors makes it difficult to study diseases, because the pathogen could impact any part of the coral-symbiont mutualism in the same ways that environmental factors do. [6]
Since corals have algal symbionts, they are considered animals and plants. This means they are impacted by both animal viruses and plant viruses. [7] [8] These plant and animal pathogens can come from marine environments, or crossover from terrestrial diseases. [3]
Little is still known about how these diseases transmit, and scientists are still researching how to control diseases and protect corals. [5] Studies do show that there is no vertical transmission in coral pathogens. This means corals do not pass diseases to their offspring through gametes, and that coral pathogens are transmitted through contagion from host-to-host. [3]
In many instances it has not been possible to identify the pathogens responsible for the disease by culturing them in the laboratory. This is because some diseases have many different kinds of bacteria associated with them. For example, 50 different bacteria varieties have been found on sites of black band disease. [3] Also, it is not always clear if fungi or bacteria present on dead necrotic tissues are caused by the disease, or if the bacteria is simply feeding on the dead tissues. [8] The way that pathogens impact corals also varies depending on the type of pathogen and species of coral. For example, cyanobacteria pathogens are able to affect the coral’s ability to do work, including blocking nitrogen fixing. This means that when coral symbionts try to change nitrogen into a usable form for the coral, pathogens will block this ability to do work. [7] Another example is a small circular single-stranded DNA (ssDNA) virus being present in association with diseased tissue on white plague disease. [8]
There are some visible signs that a coral has a disease. This includes, but is not limited to, tissue loss, abnormal coloration, and mistakes in skeleton structure. [5] These symptoms show that corals have diseases, but they can also be caused by environmental factors. Without an understanding of what cellular interactions are occurring, diseases can be difficult to diagnose. [6]
The most common way to tell if a coral is healthy is by looking at its coloration. A dead or unhealthy coral will be bleached, which means they have 40%-50% or more of their pigmentation missing. [7] Some coral diseases take the form of a narrow band of diseased tissue separating the living tissue from the exposed skeleton. The band can move across the surface of the colony at the rate of a few millimeters a day, leaving behind bleached skeletal material. [9]
The physical coloration of coral is an easy way of identifying some pathogens, since many diseases are identified by their most obvious symptoms such as black band disease, white pox and yellow-band disease. [10] Sometimes diseases look identical on a macroscopic level, and need to be identified in other ways. [3] [4] [5] For example, multiple diseases cause a break in pigmentation, which gives the coral a white band. Since a white band is a similar symptom in different diseases, identification of those diseases can be difficult. [3] In these cases the diseases are labeled through the rate at which they affect the coral. [4] [5] For white band diseases, their rates of tissue loss range from 0.1(cm/day) in white plague disease to 9(cm/d) in white band disease 2. White plague and white band disease 2 both have the same outward symptoms, but the rate at which they infect corals are drastically different, distinguishing them as different diseases. [4]
Although not a lot is known about how corals and their symbionts resist pathogens, corals do have an innate immune system. This means that corals do have some resistance to diseases. When corals are exposed to pathogens they will produce antibiotic compounds to help protect them. [5] This includes the secretion of mucus, which can harbor antibacterial properties. [7] In addition to antibiotics, corals have other natural defenses against illnesses. Phagocytosis is a cellular defense that corals use in order to target pathogens. It involves healthy cells migrating to the location of the pathogen to get rid of it through the process of phagocytosis. [5]
Although coral diseases are problematic on any reef environment, Caribbean reefs are the biggest hotspot for diseases, especially compared to Indo-Pacific reefs. [1] [10] [11] Over 70% of disease reports come from Caribbean areas, affecting 75% of hard coral species found in those areas. [1]
Coral diseases that are distributed throughout an area can have a big impact on other parts of reef communities. Not only do coral diseases impact the overall accretion and surface area of the coral, it also affects coral reproduction, the diversity and prosperity of reef species, topography of structures, and community dynamics. [1] Disease outbreaks can also shift community dynamics in reefs, where species with previously small populations could outgrow more dominant species because of disease outbreaks. Specifically, White Pox disease in the Florida Keys have impacted the prevalence of A. Palmata corals by reducing their numbers by 70%. [6] This shows that coral diseases not only impact individuals, but also have a ripple effect to entire reef communities.
Coral diseases also impact aquarists and coral laboratory settings. These diseases, however, are seemingly different from the diseases in the wild. Studies have found that some diseases impact aquarium corals, but are not an issue in the wild, and vise-versa. [1] [4] For example, red bug parasites are unique to aquariums, with no wild counterparts having been documented yet. There are also some parasitic flatworm species that infest aquarist's tanks, but are not seen in the wild. These differences in diseases in the wild and aquariums is thought to be because of the varying conditions in the two environments, including water quality and captive coral breeding. [4]
Corals and their symbionts are sensitive to environmental abiotic changes, and these environmental factors could make the corals more vulnerable to catching pathogens. Environment factors include, but are not limited to, changing ocean water temperatures, increased rainfall, more frequent storms, ocean acidification, and rising sea level. These changes in environmental factors are byproducts of climate change, which means that climate change has the potential to impact the prevalence of coral diseases. [3]
Some coral diseases show variations depending on which season it is. Patterns show that diseases are more pervasive in warmer months during the summer. Because of this, rising ocean temperatures related to climate change could be making coral diseases more prevalent, although evidence is not conclusive because of other complex factors that connect to seasonality. [3] Furthermore, the rise in sea temperature from climate change is expected to increase the frequency and severity of tropical storms. These storms do mechanical damage to reefs, through increased wave action, and stirring up and re-deposition of sediment. [2] If coral reefs are damaged, they are less likely to be able to ward off diseases due to higher levels of stress. [3]
Other stress factors related to climate change include an increase in pollution for pathogens to feed on with more rain and runoff, increased ultraviolet radiation, and a reduction in the aragonite saturation of surface seawater that is connected with ocean acidification. [1] [3] [12]
Coral diseases have the possibility to change the structures of reefs in a negative way, because one-third of corals are at risk of going extinct because of coral bleaching. [5] [6] This bleaching, partially caused by diseases, is linked to a decrease in coral cover and loss of biodiversity in reefs. [5] This rapid loss of a healthy environment has pushed conservation biologists to begin focusing more on how to help conserve coral reefs for the future.[ citation needed ]
Coral diseases are also shown to impact other parts of reef communities. They not only impact the overall accretion and surface area of the coral, they also affect coral reproduction, the diversity and prosperity of reef species, topography of structures, and community dynamics. [1] This means that coral diseases are not only an issue for individual coral colonies, but are also a danger to coral reef ecosystems as a whole.[ citation needed ]
There has been a recent push in conservation to research pathogen load on corals. If people are able to know how many pathogens a coral or environment has, then researchers will be able to better understand the health of ecosystems or individuals, and possibly predict and prevent pathogens outbreaks in the future. [5] Conservation biologists and researchers are still learning how corals interact with their environment and diseases, which are quintessential understandings needed for the conservation of corals in relation to diseases. [6]
The future conservation for coral reef diseases relies heavily on being able to quickly diagnose and implement conservation efforts towards specific coral diseases. To help with this, the Global Coral Reef Monitoring Network (GCRMN) is working to create a standardized method for identifying and labeling coral diseases. This will improve the ease of researching and publishing information on specific diseases, which would allow conservation biologists to implement conservation tactics targeting certain corals or diseases. [6]
Since researchers are still studying how diseases impact corals, it is difficult to find a “cure” that works against coral pathogens. Work has been done for treatments that work in a lab or aquarium setting, but these treatments cannot be used in the wild due to the widespread nature of corals, the cost of treatments, and considerations of how it could impact the environment. [4]
Corals are colonial marine invertebrates within the class Anthozoa of the phylum Cnidaria. They typically form compact colonies of many identical individual polyps. Coral species include the important reef builders that inhabit tropical oceans and secrete calcium carbonate to form a hard skeleton.
Coral bleaching is the process when corals become white due to loss of symbiotic algae and photosynthetic pigments. This loss of pigment can be caused by various stressors, such as changes in temperature, light, or nutrients. Bleaching occurs when coral polyps expel the zooxanthellae that live inside their tissue, causing the coral to turn white. The zooxanthellae are photosynthetic, and as the water temperature rises, they begin to produce reactive oxygen species. This is toxic to the coral, so the coral expels the zooxanthellae. Since the zooxanthellae produce the majority of coral colouration, the coral tissue becomes transparent, revealing the coral skeleton made of calcium carbonate. Most bleached corals appear bright white, but some are blue, yellow, or pink due to pigment proteins in the coral.
White band disease is a coral disease that affects acroporid corals and is distinguishable by the white band of exposed coral skeleton that it forms. The disease completely destroys the coral tissue of Caribbean acroporid corals, specifically elkhorn coral and staghorn coral. The disease exhibits a pronounced division between the remaining coral tissue and the exposed coral skeleton. These symptoms are similar to white plague, except that white band disease is only found on acroporid corals, and white plague has not been found on any acroporid corals. It is part of a class of similar disease known as "white syndromes", many of which may be linked to species of Vibrio bacteria. While the pathogen for this disease has not been identified, Vibrio carchariae may be one of its factors. The degradation of coral tissue usually begins at the base of the coral, working its way up to the branch tips, but it can begin in the middle of a branch.
Black band disease is a coral disease in which corals develop a black band. It is characterized by complete tissue degradation due to a pathogenic microbial consortium. The mat is present between apparently healthy coral tissue and freshly exposed coral skeleton.
The Staghorn coral is a branching, stony coral, within the Order Scleractinia. It is characterized by thick, upright branches which can grow in excess of 2 meters in height and resemble the antlers of a stag, hence the name, Staghorn. It grows within various areas of a reef but is most commonly found within shallow fore and back reefs, as well as patch reefs, where water depths rarely exceed 20 meters. Staghorn corals can exhibit very fast growth, adding up to 5 cm in new skeleton for every 1 cm of existing skeleton each year, making them one of the fastest growing fringe coral species in the Western Atlantic. Due to this fast growth, Acropora cervicornis, serve as one of the most important reef building corals, functioning as marine nurseries for juvenile fish, buffer zones for erosion and storms, and center points of biodiversity in the Western Atlantic.
Elkhorn coral is an important reef-building coral in the Caribbean. The species has a complex structure with many branches which resemble that of elk antlers; hence, the common name. The branching structure creates habitat and shelter for many other reef species. Elkhorn coral is known to grow quickly with an average growth rate of 5 to 10 cm per year. They can reproduce both sexually and asexually, though asexual reproduction is much more common and occurs through a process called fragmentation.
White pox disease, first noted in 1996 on coral reefs near the Florida keys, is a coral disease affecting Elkhorn coral throughout the Caribbean. It causes irregular white patches or blotches on the coral that result from the loss of coral tissue. These patches distinguish white pox disease from white band disease which produces a distinctive white band where the coral skeleton has been denuded. The blotches caused by this disease are also clearly differentiated from coral bleaching and scars caused by coral-eating snails. It is very contagious, spreading to nearby coral.
Coral reef protection is the process of modifying human activities to avoid damage to healthy coral reefs and to help damaged reefs recover. The key strategies used in reef protection include defining measurable goals and introducing active management and community involvement to reduce stressors that damage reef health. One management technique is to create Marine Protected Areas (MPAs) that directly limit human activities such as fishing.
Human activities have substantial impact on coral reefs, contributing to their worldwide decline.[1] Damaging activities encompass coral mining, pollution, overfishing, blast fishing, as well as the excavation of canals and access points to islands and bays. Additional threats comprise disease, destructive fishing practices, and the warming of oceans.[2] Furthermore, the ocean's function as a carbon dioxide sink, alterations in the atmosphere, ultraviolet light, ocean acidification, viral infections, the repercussions of dust storms transporting agents to distant reefs, pollutants, and algal blooms represent some of the factors exerting influence on coral reefs. Importantly, the jeopardy faced by coral reefs extends far beyond coastal regions. The ramifications of climate change, notably global warming, induce an elevation in ocean temperatures that triggers coral bleaching—a potentially lethal phenomenon for coral ecosystems.
Pavona duerdeni, the porkchop coral, is a coral that forms clusters of cream-colored lobes or discs. They grow in large colonies, divided into ridges or hillocks. The coral is considered to be uncommon due to its low confirmed abundance, yet they are more commonly found in Hawaii, the Indo-Pacific, and the Tropical Eastern Pacific. They make up some of the largest colonies of corals, and have a slow growth rate, as indicated by their dense skeletons. Their smooth appearance is due to their small corallites growing on their surface.
Coral aquaculture, also known as coral farming or coral gardening, is the cultivation of corals for commercial purposes or coral reef restoration. Aquaculture is showing promise as a tool for restoring coral reefs, which are dying off around the world. The process protects young corals while they are most at risk of dying. Small corals are propagated in nurseries and then replanted on the reef.
The resilience of coral reefs is the biological ability of coral reefs to recover from natural and anthropogenic disturbances such as storms and bleaching episodes. Resilience refers to the ability of biological or social systems to overcome pressures and stresses by maintaining key functions through resisting or adapting to change. Reef resistance measures how well coral reefs tolerate changes in ocean chemistry, sea level, and sea surface temperature. Reef resistance and resilience are important factors in coral reef recovery from the effects of ocean acidification. Natural reef resilience can be used as a recovery model for coral reefs and an opportunity for management in marine protected areas (MPAs).
Galaxea fascicularis is a species of colonial stony coral in the family Euphylliidae, commonly known as Octopus coral, Fluorescence grass coral, and Galaxy coral among various vernacular names.
The hologenome theory of evolution recasts the individual animal or plant as a community or a "holobiont" – the host plus all of its symbiotic microbes. Consequently, the collective genomes of the holobiont form a "hologenome". Holobionts and hologenomes are structural entities that replace misnomers in the context of host-microbiota symbioses such as superorganism, organ, and metagenome. Variation in the hologenome may encode phenotypic plasticity of the holobiont and can be subject to evolutionary changes caused by selection and drift, if portions of the hologenome are transmitted between generations with reasonable fidelity. One of the important outcomes of recasting the individual as a holobiont subject to evolutionary forces is that genetic variation in the hologenome can be brought about by changes in the host genome and also by changes in the microbiome, including new acquisitions of microbes, horizontal gene transfers, and changes in microbial abundance within hosts. Although there is a rich literature on binary host–microbe symbioses, the hologenome concept distinguishes itself by including the vast symbiotic complexity inherent in many multicellular hosts. For recent literature on holobionts and hologenomes published in an open access platform, see the following reference.
A mesophotic coral reef or mesophotic coral ecosystem (MCE), originally from the Latin word meso (meaning middle) and photic (meaning light), is characterized by the presence of both light-dependent coral and algae, and organisms that can be found in water with low light penetration. Mesophotic coral ecosystems occur at depths beyond those typically associated with coral reefs as the mesophotic ranges from brightly lit to some areas where light does not reach. Mesophotic coral ecosystem (MCEs) is a new, widely-adopted term used to refer to mesophotic coral reefs, as opposed to other similar terms like "deep coral reef communities" and "twilight zone", since those terms sometimes are confused due to their unclear, interchangeable nature. Many species of fish and corals are endemic to the MCEs making these ecosystems a crucial component in maintaining global diversity. Recently, there has been increased focus on the MCEs as these reefs are a crucial part of the coral reef systems serving as a potential refuge area for shallow coral reef taxa such as coral and sponges. Advances in recent technologies such as remotely operated underwater vehicles (ROVs) and autonomous underwater vehicles (AUVs) have enabled humans to conduct further research on these ecosystems and monitor these marine environments.
Hologenomics is the omics study of hologenomes. A hologenome is the whole set of genomes of a holobiont, an organism together with all co-habitating microbes, other life forms, and viruses. While the term hologenome originated from the hologenome theory of evolution, which postulates that natural selection occurs on the holobiont level, hologenomics uses an integrative framework to investigate interactions between the host and its associated species. Examples include gut microbe or viral genomes linked to human or animal genomes for host-microbe interaction research. Hologenomics approaches have also been used to explain genetic diversity in the microbial communities of marine sponges.
Stony coral tissue loss disease (SCTLD) is a disease of corals that first appeared off the southeast coast of Florida in 2014. It originally was described as white plague disease. By 2019 it had spread along the Florida Keys and had appeared elsewhere in the Caribbean Sea. The disease destroys the soft tissue of at least 22 species of reef-building corals, killing them within weeks or months of becoming infected. The causal agent is unknown but is suspected to be either a bacterium or a virus with a bacterium playing a secondary role. The degree of susceptibility of a coral, the symptoms, and the rate of progression of the disease vary between species. Due to its rapid spread, high mortality rate, and lack of subsidence, it has been regarded as the deadliest coral disease ever recorded, with wide-ranging implications for the biodiversity of Caribbean coral reefs.
The environmental impact of recreational diving is the effects of recreational scuba diving on the underwater environment, which is largely the effects of diving tourism on the marine environment. It is not uncommon for highly trafficked dive destinations to have more adverse effects with visible signs of diving's negative impacts due in large part to divers who have not been trained to sufficient competence in the skills required for the local environment, an inadequate pre-dive orientation, or lack of a basic understanding of biodiversity and the delicate balance of aquatic ecosystems. There may also be indirect positive effects as the environment is recognised by the local communities to be worth more in good condition than degraded by inappropriate use, and conservation efforts get support from dive communities who promote environmental awareness, and teach low impact diving and the importance of respecting marine life. There are also global coral reef monitoring networks in place which include local volunteer divers assisting in the collection of data for scientific monitoring of coral reef systems, which may eventually have a net positive impact on the environment.
Jamaica, an island located within the Caribbean Sea, known for being a popular tourist destination because of its pristine white sand beaches, is now faced with the issue of mass coral depletion. Both environmental and human factors contribute to the destruction of these corals, which inevitably affect Jamaica's environmental sustainability and economy. Actions have been put in place to counteract the negative consequences associated with the loss of the corals, which act as a symbol of hope for the revival of Jamaica's environment.
All animals on Earth form associations with microorganisms, including protists, bacteria, archaea, fungi, and viruses. In the ocean, animal–microbial relationships were historically explored in single host–symbiont systems. However, new explorations into the diversity of marine microorganisms associating with diverse marine animal hosts is moving the field into studies that address interactions between the animal host and a more multi-member microbiome. The potential for microbiomes to influence the health, physiology, behavior, and ecology of marine animals could alter current understandings of how marine animals adapt to change, and especially the growing climate-related and anthropogenic-induced changes already impacting the ocean environment.