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Ocean Literacy

Saving Our Oceans Through Coral Restoration

 

Saving our oceans from the devastating impacts of human choices is possible through coral restoration. Often it can be difficult to know how to aid our oceans in recovery, yet several restoration opportunities exist. While scientists work diligently to help coral reefs recover, societal knowledge and influence is the key to true change.

Loss of Coral Reefs

Humans contribute approximately 40 billion pounds of carbon dioxide to our atmosphere each year through routine activities (Block, 2017). Since the Industrial Revolution, our earth has warmed by 0.7 degrees Celsius due to the amount of carbon dioxide released (Riebeek, 2010). It is estimated that over the next 80 years warming will increase by 2-6 degrees celsius, impacting life on land and life within our oceans (Riebeek, 2010). Approximately 93% of the carbon dioxide put into the atmosphere is absorbed by our oceans, allowing earth’s temperatures to remain stable.  Without a healthy ocean, stability will be compromised, resulting in weather pattern changes and a loss of biodiversity among both plants and animals (Block, 2017).

Coral reefs occupy less than 1% of our oceans, but house more than 25% of our ocean’s fishes (NOAA’s Coral Reef Conservation Program, 2016). They require specific water temperatures in order to survive, exhibiting coral bleaching when ocean temperatures rise above their thresholds. A symbiotic relationship exists between corals and zooxanthellae, a type of algae. This gives corals with their vibrant colors and provides organic material that corals use for growth (US Department of Commerce, National Oceanic and Atmospheric Administration, 2013). During coral bleaching the algae is expelled by the coral, causing the coral tissues to become white. Frequently leading to coral death when the stress is extended, corals are unable to recover the algae to the coral’s tissues. 

Restoration Opportunities

Humans need to understand how we alter our earth and how coral restoration efforts can benefit our oceans. Both proactive and reactive measures are possible in support of coral restoration. Proactive avenues include Marine Protected Areas (MPAs) and educating the public, which require varying levels of community and government support (Gunderson, 2007; Rinkevich, 2008; Yeemin, Sutthacheep, & Pettongma, 2006). Reactive conservation is working to fix an immediate problem, rather than preemptively working to protect a species or ecosystem. This avenue is more common for restoring ecosystems rather than specific species. There are several techniques utilized for reactive conservation with corals, including silviculture, artificial reefs, and alternative management strategies. While each opportunity has its benefits and drawbacks, there are a variety of approaches to coral restoration.

Marine Protected Areas

MPAs are marine areas being preserved and protected against human harm in regards to animal, shell, and substrate collection. Even so, there are MPAs that allow for collection upon specific circumstances and needs of the ecosystem being conserved. There is the question of whether or not MPAs actually benefit the intended species, area, or ecosystem. While MPAs are a good effort in restoring damaged ecosystems, there isn’t evidence to support MPAs actually benefiting intended organisms (Rinkevich, 2008). Often MPAs are not beneficial because they are inadequately managed, therefore making their purpose moot (Rinkevich, 2008). If the restrictions of MPAs were effectively enforced and respected by humans, their benefit would be greater (International Coral Reef Initiative, 2017; World Wildlife Fund, 2017).  This would ultimately preserve the coral reefs and other species that live within them. Respecting the restrictions of MPAs requires support from local and national governments, as well as from the local people. Human disrespect for the environment is often unintentional, as it is a lack of knowledge about the needs of an ecosystem.

Educating the Public

There is a prevailing disconnect between the scientific community and the general public. This can be seen in areas where locals are seemingly unaware of conservation efforts necessary in their communities. Typically, columnists and officials promote scientific findings through the negative and uninspiring lens of species loss and habitat fragmentation (Gunderson, 2007). This leads the public to a sense of hopelessness and inability to impact conservation efforts (Gunderson, 2007). Once the public is inspired, coral restoration efforts can achieve remarkable success with the aid of public involvement. A great example is a coral reef restoration project in Thailand was executed off of Kham Island (Yeemin et al., 2006). Youth took direct action by  transplanting coral fragments with a success rate of over 90% (Yeemin et al., 2006). Thailand’s coral restoration efforts demonstrated youth’s active voice and important role in how our earth is treated (Yeemin et al., 2006). Ultimately, some researchers argue that local involvement is a key component in effective coral restoration and their reef ecosystems (Yeemin et al., 2006).

Artificial Reefs

Artificial reefs are uncommonly documented and have benefits that spread ecosystem-wide. Creating an artificial reef requires fibreglass pieces to be placed into the ecosystem, creating opportunities for new corals to establish (Ng, Toh, & Chou., 2016). This endeavor is successful, with over 100 species demonstrating a positive increase in population size over 10 years (Ng, Toh, & Chou., 2016). Because fibreglass pieces are plastics, how will they affect the ecosystem post coral establishment. With this consideration and a lack of research on these artificial reefs, hesitation towards this approach is understandable. 

Ng, Toh, & Chou (2016) utilize a method adding plastics to our oceans, allowing for potential toxins to be leached into our environment. With toxins in our oceans, the organisms that live within it are more likely to ingest such toxins. As the individuals ingest toxins throughout their lifespan, a process known as bioaccumulation, the overall health of the individual decreases (Environmental Protection Agency, 2002). When individuals affected by bioaccumulation are consumed by organisms higher on the food chain, the consumers become affected by biomagnification. Biomagnification is where the amount of a toxin within an individual is a higher concentration further up the food chain (Environmental Protection Agency, 2002). As scientists, we should be looking for methods that help restore ecosystems without adding more toxins to the environment. 

Restoring Fish Populations

Another reactive approach, restoring fish populations to increase corals have more potential for success in regards to reef ecosystems.The removal of apex predators from ecosystems creates imbalances which allows the populations of lower level species to overpopulate (Heithaus et al., 2008). To reduce populations of lower level species to healthy numbers, top predator populations need to be restored (Heithaus et al., 2008). Prohibiting overfishing of apex predators is necessary for reef recovery as these species are the least able to recover (Dulvy & Kindsvater, 2015). Prohibiting the use of equipment and fishing practices can be ineffective (Rinkevich, 2008). These measures are taxing and not well managed by the associated governments (Rinkevich, 2008). Dulvy & Kindsvater (2015) work to restore corals and reef ecosystems with the use of fish population restoration. However, it has not been shown to be as effective as creating an artificial reef (Dulvy & Kindsvater, 2015). Further research is needed to determine if restored populations will continue living in an environment being restored. A concern is that restored populations with either die-off quickly or relocate to a location with acceptable resources already intact.

Silviculture

Through silviculture, small pieces of coral are clipped and farmed (in situ, ex situ, or both) (Epstein, Bak, & Rinkevich, 2001; Epstein, Bak, & Rinkevich, 2003; Shafir, Rijn, & Rinkevich, 2006). After, they are returned to the damaged reef to live, continue reproducing, and provide resources to other species (Epstein, Bak, & Rinkevich, 2001; Epstein, Bak, & Rinkevich, 2003; Shafir, Rijn, & Rinkevich, 2006). One consideration is whether to focus on sexually or asexually reproducing species. Rinkevich (2000) tested fragments of two Acropora subspecies and found that asexually reproducing Acropora digitifera performed better than sexually reproducing Acropora hyacinthus. Similarly, asexually reproducing Acropora spp. performed greater than sexually reproducing Acropora spp (Boch & Morse, 2012). Important factors to consider beyond coral itself are water speed and quality, which affect coral material. One approach is treating reefs similarly to forests, where dead areas are evaluated and restored based on ecosystem needs (Epstein et al., 2003). This requires ecosystem evaluation prior to transplantation.  

Technique adaptability (the ability for a technique to be used across genuses) is important in restoring corals through silviculture. Stylophora pistillata and Acropora spp. are utilized in multiple studies each, with Pocillopora damicornis appearing once (Boch & Morse, 2012; Epstein et al., 2001; Rinkevich, 2000; Shafir et al., 2006). Acropora spp. is most commonly utilized in coral restoration and appears to have the highest success rates. A lack of success among S. pistillata and P. damicornis, demonstrates the need for easily modifiable techniques across genuses (Boch & Morse, 2012; Epstein et al., 2001; Rinkevich, 2000; Shafir et al., 2006). To restore entire coral ecosystems, research of restoration efforts of other coral species beyond Acropora spp. are vital.

Looking Forward

Proactive coral restoration poses greater promise for future environmental health compared to more common reactive efforts. Each restoration technique requires an understanding of the effort required to benefit the health, growth, and success of our corals. Coral restoration efforts allow for healthier reef ecosystems and oceans, and scientists need our help to advocate for our ocean. After inspiring ocean advocates, we can build on the knowledge of local environments, then expand upon it to the entire ocean. After creating reef advocates, we should promote reef-friendly changes in human habits and focus on restoring reefs as an ecosystem. These ecosystem-focused restoration techniques should involve restoration of several species within our reefs, including fish that live within them.

Stacy Craft, B.S.

M.A. Student, Project Dragonfly – Miami University, Oxford, OH

Instructional Aide, T.E.R.I., Inc., San Marcos, CA

Educator, Sea Life Aquarium, Carlsbad, CA

Instructor, Helen Woodward Animal Center, Rancho Santa Fe, CA

Correspondence can be sent to Stacy Craft B.S. by email at craftsl@miamioh.edu or by phone to (909) 342-3995.

Acknowledgement: Stacy Craft B.S. completed this project as a part of her graduate work with Project Dragonfly at Miami University in Oxford, Ohio in conjunction with San Diego Zoo Global. She would like to thank Project Dragonfly students and staff that helped with editing her work, with special thanks to Emily Craft for support throughout this process.

Resources

  • Block, B. (2017, September). Oceans absorb less carbon dioxide as marine systems change. 
  • Retrieved September 27, 2017, from http://www.worldwatch.org/node/6323 Boch, C. A., & Morse, A. N. C. (2012). Testing the effectiveness of direct propagation techniques for coral restoration of Acropora spp. Ecological Engineering, 40, 11-17.
  • Dulvy, N. K., & Kindsvater, H. K. (2015). Recovering the potential for coral reefs. Nature, 520304-305.
  • Environmental Protection Agency. (2002). Bioaccumulation / biomagnification effects. RetrievedOctober 23, 2017, from https://www.epa.gov/sites/production/files/documents/bioaccumulationbiomagnificationeffects.pdf 
  • Epstein, N., Bak, R. P. M., & Rinkevish, B. (2001). Strategies for gardening denuded coral reef areas: The applicability of using different types of coral material for reef restoration. Restoration Ecology, 9, 432-442.
  • Epstein, N., Bak, R. P. M., & Rinkevish, B. (2003). Applying forest restoration principles to coral reef rehabilitation. Aquatic Conservation: Marine and Freshwater Ecosystems, 13387-395.
  • Gunderson, L. (2007). Ecology: A different route to recovery for coral reefs. Current Biology, 17R28.
  • Heithaus, M. R., Frid, A., Wirsing, A. J., & Worm, B. (2008). Predicting ecological consequences of marine top predator declines. ScienceDirect, 23, 202-210.
  • International Coral Reef Initiative. (2017). Status of and threat to coral reefs. Retrieved October 23, 2017, from http://www.icriforum.org/about-coral-reefs/status-and-threat-coral-reefs
  • Ng, C. S. L., Toh, T. C., & Chou, L. M. (2016). Coral restoration in Singapore’s sediment-challenged sea. Regional Studies in Marine Science, 8, 422-429.
  • NOAA’s Coral Reef Conservation Program. (2016, September 10). Existing and potential value of coral ecosystems with respect to income and other economic values. Retrieved October 01, 2017, from https://coralreef.noaa.gov/aboutcorals/values/biodiversity/ 
  • Riebeek, H. (2010). Global warming. Retrieved September 27, 2017, from https://earthobservatory.nasa.gov/Features/GlobalWarming/page5.php
  • Rinkevich, B. (2000). Steps towards the evaluation of coral reef restoration by using small branch fragments. Maine Biology, 136, 807-812.
  • Rinkevich, B. (2008). Management of coral reefs: We have gone wrong when neglecting active reef restoration. Marine Pollution Bulletin, 56, 1821-1824.
  • Shafi, S., Rijn, J. V., & Rinkevich, B. (2006). Steps in the construction of underwater coral nursery an essential component in reef restoration acts. Marine Biology, 149, 679-687.
  • US Department of Commerce, National Oceanic and Atmospheric Administration. (2013, June 01). Corals. Retrieved October 23, 2017, from https://oceanservice.noaa.gov/education/tutorial_corals/coral02_zooxanthellae.html
  • World Wildlife Fund. (2017). Coral reefs: Threats. Retrieved October 23, 2017, from http://wwf.panda.org/about_our_earth/blue_planet/coasts/coral_reefs/coral_threats/
  • Yeemin, T., Sutthacheep, M., & Pettongma, R. (2006). Coral reef restoration projects in Thailand. Ocean & Coastal Management, 49, 562-575.

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Aquacultures & Fisheries

What the Fish Are Telling Us About Marine Biodiversity and Ocean Health Around Tenerife

Tenerife sits in the eastern Atlantic like a crossroads. Positioned roughly 300 kilometres off the northwest coast of Africa, the island intersects the paths of the Canary Current, warm subtropical surface waters, and the deep cold upwellings of the Atlantic basin. The result is one of the most ecologically productive marine environments in the northern hemisphere, a place where bluefin tuna from the Mediterranean share waters with tropical reef species and migratory whales from the polar ocean. What lives in these waters, and how those populations are changing, tells us something important about the health of the broader Atlantic system.

The Anatomy of an Exceptional Marine Environment

The waters around Tenerife support approximately 400 species of fish, a number that reflects the unusual convergence of marine provinces that the island straddles. [1] Its seafloor topography is dramatic: the island drops away steeply from the coast, reaching oceanic depths within just a few kilometres of shore. This proximity of shallow coastal habitat to very deep water creates conditions that support both reef-associated species and the large pelagic predators of the open ocean, sometimes within sight of the same beach.

In the deeper offshore waters, the Canary Islands are internationally recognised as one of the finest big game fishing destinations in the world, and for good reason. Atlantic bluefin tuna (Thunnus thynnus) pass through in their thousands between December and April, migrating northward toward Mediterranean spawning grounds. These are not small fish. Individuals regularly exceed 250 kilograms, and the largest bluefin recorded in these waters approach 450 kilograms. [2] Their spring passage coincides with dense schools of Atlantic mackerel (Scomber scombrus) and smaller baitfish that concentrate near the island, drawing the giants in from the open Atlantic.

Blue marlin (Makaira nigricans) and white marlin (Kajikia albida) are present from spring through autumn, the two billfish species that define Tenerife’s reputation among dedicated sport anglers. Spearfish (Tetrapturus belone) inhabit the deeper offshore trenches. Yellowfin tuna (Thunnus albacares), bigeye tuna (Thunnus obesus), wahoo (Acanthocybium solandri), and mahi-mahi (Coryphaena hippurus) complete a pelagic assemblage that few locations outside the tropics can match. [2]

Closer to shore, the volcanic reef structures support a different community. Atlantic amberjack (Seriola dumerili), barracuda (Sphyraena viridensis), grouper (Epinephelus spp.), and European sea bass (Dicentrarchus labrax) inhabit the rocky substrates, alongside numerous wrasse species, bream, and moray eels. The deeper sandy bottoms, where slow-jigging techniques are most effective, hold species less visible to tourists but central to local gastronomy: red porgy (Pagrus pagrus), sargo (Diplodus sargus), and various sparids that have been fished by Canarian communities for centuries. [3]

Reading the Signals: What Is Changing

The richness of this marine environment is not static, and the signals coming from the water are mixed. On one hand, the resident cetacean populations tell a story of relative stability. Whale Watch Tenerife, which has logged cetacean sightings systematically since 2018, recorded 17 different species in both 2018 and 2023, with short-finned pilot whales (Globicephala macrorhynchus) and bottlenose dolphins (Tursiops truncatus) present on nearly every survey day. [4] In 2025, orca sightings and encounters with fin whales were notable additions to the year’s record. [4] The continued presence of these apex predators is generally a positive indicator of ecosystem function.

On the other hand, the EU-funded OCEAN CITIZEN restoration project documented concerning trends at the base of the food web when it began its work on the island in 2024. Fish populations associated with rocky reef habitats have declined significantly compared to historical baselines. Seagrass meadows (Cymodocea nodosa), which serve as nurseries for juvenile fish and feeding grounds for sea turtles, have retreated across multiple coastal areas due to sedimentation, pollution, and rising water temperatures. Rocky reefs have been degraded by a combination of physical disturbance and the effects of ocean acidification. [5] These are not peripheral problems. Reef habitats and seagrass meadows are foundational to the productivity that ultimately supports the entire marine food web, from the smallest reef fish to the bluefin tuna and the pilot whales that hunt above them.

The Atlantic regulatory framework governing commercial fishing has also evolved. EU fisheries ministers, meeting in December 2025, set 2026 catch limits with 81 percent of total allowable catches in the northeast Atlantic at maximum sustainable yield levels — an improvement on previous years, though the failure to agree a mackerel quota for 2026 due to disputes with non-EU countries was a notable setback. [6] For sport and recreational fishing around Tenerife, a growing culture of catch and release has taken hold among charter operators, particularly for bluefin tuna, billfish, and other large pelagic species. Most reputable charters now apply mandatory release for bluefin tuna, reflecting both changing regulation and a shift in the values of visiting anglers. [3]

What the Fish Are Actually Telling Us

Marine ecosystems are exceptionally good at communicating ecological stress, if we know how to listen. The presence of 28 cetacean species, including year-round resident pilot whales, tells us that the deep-water food web west of Tenerife remains productive. The decline of reef fish populations and seagrass cover tells us that the shallower coastal zone is under sustained pressure from human activity. The continued migration of bluefin tuna past the island tells us that large-scale Atlantic management is beginning to take effect after decades of overfishing. The appearance of orcas and large baleen whales in 2025 tells us that the waters retain the biological richness to attract ocean wanderers from across the hemisphere.

Tenerife’s marine environment is neither pristine nor beyond recovery. It occupies a contested middle ground where genuinely exceptional natural heritage coexists with the pressures of one of Europe’s busiest tourist destinations. Paying attention to what lives here, in all its scientific specificity, is the first step toward deciding what kind of relationship the island will have with its sea.

Sources

  1. Wikipedia: Tenerife — fauna and marine ecology
  2. FishingBooker: Tenerife Fishing — The Complete Guide for 2026, fishingbooker.com, January 2026
  3. FishingBooker: Canary Islands Fishing — The Complete Guide for 2026, fishingbooker.com
  4. Whale Watch Tenerife: Tenerife Whale Watching Season — cetacean sighting data 2023-2025, whalewatchtenerife.org
  5. OceanCitizen EU: Reclaiming Tenerife’s Ocean, oceancitizen.eu, September 2024
  6. European Commission Oceans and Fisheries: Fisheries ministers agree fishing opportunities for 2026, December 2025, oceans-and-fisheries.ec.europa.eu
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