Satellites orbiting Earth offer great potential to better understand the world’s reefs over time beyond the sites visited by researchers
University of Queensland research has found
PhD candidate David E. Carrasco Rivera from UQ’s School of Environment analysed thousands of images from 20 years of field studies and satellites captured of Heron Reef
“Most of what we know about world’s reefs comes from field data
which is done in less than 0.1 per cent of the actual reef area,” Mr Carrasco Rivera said
“That’s like completing a full body assessment by only looking at a portion of your finger
“Our study found using satellite imagery gives researchers the ability to continually monitor the reef and identify trends in the environment beyond the areas visited
“By combining machine learning with the image data sets
we created annual maps of reef composition over 2 decades
“Satellite imagery will never replace field data completely
but many reefs are too big and remote to visit every square metre due to research funding constraints and weather conditions.”
Mr Carrasco Rivera used the field photos to estimate and map how much sand
rock and coral was present in the areas where satellite photos were only taken
Associate Professor Chris Roelfsema has led a monitoring program at Heron Reef that has been ongoing for more than 20 years
He said understanding the entirety of the reef over time is vital to making appropriate conservation and management decisions
“We look at ourselves in the mirror daily so we can identify small changes in appearance when we are sick
we need to see it regularly to notice changes,” Dr Roelfsema said
“Consistent and ongoing monitoring is a key contributor to understanding what a normal environment cycle is
or if another factor is leading to changes including coral cover variations and colour
“This review shows satellites allow us to do this with 59 to 81 per cent accuracy depending on environmental conditions
“The study found satellite data was accurate enough to supplement field data for up to 3 years if researchers can’t get out in the water for that period
“If you can only get out to a very small part of the reef
and if you don’t have information before the event then it’s hard to understand the impact or to assess the recovery.”
Dr Roelfsema said the study was possible through the facilities of UQ’s Heron Island Research Station
“Access to the permanent research station meant we were able to consistently monitor the surrounding reef for 2 decades whereas many projects struggle to have easy access to the reef,” he said
“These remote sensing findings have scope to benefit reefs across the globe as they continue to be impacted by climate change.”
The research was published in Remote Sensing
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Last week, the International Coral Reef Initiative (ICRI)
a global partnership and forum of 100-plus governments
and other entities working toward the preservation of the world’s coral reefs and their associated ecosystems
announced that it has recorded the worst coral bleaching event on record
with 84% of the world’s reefs showing effects
Coral bleaching is a broad term conceived back in 1998 after the phenomenon was first widely noticed—or at least seriously and widely recognized—that essentially describes critically stressed corals
which turn white due to inhospitable changes in temperature and pH level
The fourth global bleaching event on record since 1998
has just seriously outdone the previous event from 2014-2017 and affected about two-thirds of the world’s reefs
This current crisis is blamed on the average of ocean temperatures away from the poles
which has seen back-to-back record highs just at or above the 2.7-degree Fahrenheit (1.5-degree-Celsius) “warming limit” above “pre-industrial,” or average global ocean temperatures between 1850 and 1900 A.D.
which calculated the highest of those numbers: 2.9 degrees Fahrenheit (or 1.6 Celsius)
“We’re seeing forecasts that temperatures are going to continue to stay high,” Mark Eakin, corresponding secretary for the International Coral Reef Society and retired chief of NOAA’s Coral Reef Watch program, told the Associated Press
“We just may never see the heat stress that causes bleaching dropping below the threshold that triggers a global event
so this may be the last one… We’re looking at something that’s completely changing the face of our planet and the ability of our oceans to sustain lives and livelihoods,” Eakin added
What’s a lowly surf rat left to do in the here and now
and manual and/or analog paddling of said surfboards may be about the best most of us can offer our great giver
“The best way to protect coral reefs,” Eakin puts forth
“is to address the route cause of climate change
and that means reducing the emissions—the human emissions—that are mostly from the burning of fossil fuels
Everything else is looking like a Band-Aid rather than a solution.”
convoluted little term oft-hawked by libertarians and neoliberals
Love or hate the ocean and its temperature-dependent multitude of critters
continue to vote with those John Wayne dollars as always
but it’s up to the nerds whose direction is at the discretion of the energy geezers and geezettes to sort out both us and our beloved reefs
Strong correlations have been drawn between a rise in the population of sharks on Ashmore Reef
off the north-west coast of Western Australia and an increase in other large and mid-sized predatory reef fish alongside the decline in smaller species
The return of apex predators like sharks can restore the critical ecological balance to coral reef ecosystems
creating healthier and more abundant environments
a new collaborative study between researchers in the UK and Australia has found
The study – a joint effort between the University of Glasgow, University of Western Australia’s Ocean Institute, and the Australian Institute of Marine Science – has been published in the scientific journal, Animal Ecology
It details a project through which researchers analysed video footage captured using baited remote underwater video systems before the enforcement of the area’s ‘no-take’ status in 2004
when there were few sharks within the area
This was then compared to footage captured in 2016
scientists discovered that small mesopredatory reef fish exhibited anti-predator behaviours – including less foraging for food – when they were under threat by larger predators
An overabundance of any species can disrupt the ecosystem balance in a coral reef
a large and unchecked population of small mesopredatory fish can have impacts down the food chain
with essentially free reign to over-consumer young fish or invertebrates leading to the decimation of their numbers
Under the watchful eye of an apex predator
It’s precisely what researchers observed in the case of Ashmore Reef
presenting their findings as ‘how reefs should function’ when they are in relatively pristine conditions
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It all offers a deeper insight into the role that big predators such as sharks play in maintaining these ecosystems – essential information when it comes to improving the resilience and survival of reefs
and Environmental Change at the University of Glasgow
said: “This study really shows the importance of conserving top predators like sharks
it restores critical ecological interactions that are vital for healthy marine ecosystems
“Removing large predators and allowing mesopredators to proliferate can destabilize ecological balance
leading to unpredictable changes in species abundance and interactions that can negatively affect overall reef health.”
These findings have been echoed in a similar study spanning two-decades looking into the gradual disappearance of Great white sharks from False bay in South Africa
Great white sharks have experienced a dramatic decline and subsequent disappearance over the last 20 years
with the finger of blame being directed at a combination of factors
including decades of unsustainable capture in nets and some more recent instances of predation by orcas
In this study – similar to the findings in Ashmore Reef – the loss of the apex predator gave greater space to mesopredators which in turn led to the stark over-consumption of smaller fish and prey species
It all illustrates the ripple effect that losing a top ocean predator can have on an ecosystem already walking a fine line of equilibrium
Dr Mark Meekan from the University of Western Australia’s Ocean Institute
said: “Reef shark populations on Ashmore Reef have increased significantly since effective enforcement of the no-take Marine Protected Area status of the reef started in 2008
“This has enabled us to examine how these large predators have the potential to structure reef communities through the behavioural effects they have on their prey
fearful prey reacts to an increase in predation risk by exhibiting traits to reduce exposure
“These responses can alter the prey’s behaviour so they spend much more time avoiding predators
which limits the amount of time they have available for important activities
including reproduction and foraging – when they forage they may be forced into poor quality habitats.”
The work now contributes to a growing body of evidence to support the idea that predators have important indirect effects on other species in food chains by triggering in them behaviours in prey that attempt to lower their risk of predation
The study – Recovery of Reef Shark Populations Invokes Anti-Predator Behaviours in Mesopredatory Reef Fish in a Coral Reef – is published in the scientific journal
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Through the Mesoamerican Reef Fund initiative MAR+Invest the GFCR is providing technical advice and financing to 50 early-stage
reef-friendly businesses from countries in the region
The work spans 1.7 million hectares of coral reefs and is creating economic opportunities for 15,000 people.
"Investing in local organizations with deep-rooted knowledge and experience in coral reef conservation is critical for protecting the Mesoamerican Reef and for achieving the UN’s Sustainable Development Goals,” says Susan Gardner
“These local organizations are uniquely positioned because people benefit directly from healthy reefs
providing families with better nutrition and higher incomes
education and building resilience.”
One of the projects MAR+Invest supports focuses on raising juvenile king crabs and releasing them onto reefs to combat the overgrowth of macroalgae
which thrives due to rising ocean temperatures associated with climate change
have voracious algae appetites and can help control algae without harming coral
their low natural population density limits their impact
this project aims to restore balance to the ecosystem
benefiting coral health and providing a sustainable income source for local fishers.
To combat pollution, another major threat to corals, the Mesoamerican Reef Fund is helping the Royal Mayan Shrimp Farm in Belize become more sustainable
Traditional shrimp farms often spew polluted water into the ocean and cut down mangrove forests
Meanwhile in Mexico, MAR+Invest is supporting a company, CarbonWave, which turns a type of seaweed known as sargassum into raw materials for various products
This prevents sargassum from smothering corals and wildlife or ending up in landfills where it decays
potentially polluting groundwater.
The die off has been driven by rising sea temperatures
pollution and unsustainable fishing practices.
The Global Fund for Coral Reefs is a UN-backed multi-partner trust fund. It provides grants and loans to coral-reef-positive enterprises worldwide, supporting initiatives from ecotourism to sustainable aquaculture to seaweed farming. The GFCR’s goal is to support over 400 reef-positive businesses and create more than 30,000 jobs by 2030
the Mesoamerican Reef Fund is aiming to leverage US$60 million in private capital and enhance the resilience of over 3 million coastal residents.
Each reef-positive enterprise in the GFCR’s pipeline addresses threats to reef health while supporting poverty alleviation and contributing to the financial sustainability of marine protected areas
“The fund’s projects show that even modest investments in biodiversity conservation can unlock remarkable innovation and impact,” says UNEP’s Susan Gardner
“In the face of mounting threats to coral reefs
this multiplying effect is exactly what we need right now.”
The Kunming-Montreal Global Biodiversity Framework
The planet is experiencing a dangerous decline in nature. One million species are threatened with extinction, soil health is declining and water sources are drying up. The Kunming-Montreal Global Biodiversity Framework sets out global targets to halt and reverse nature loss by 2030
It was adopted by world leaders in December 2022
To address the drivers of the nature crisis
UNEP is working with partners to take action in landscapes and seascapes
The Global Fund for Coral Reefs (GFCR) was established to accelerate urgent investment and action to enhance the resilience of coastal reef ecosystems
The GFCR comprises two major financial vehicles: a UN-led grant fund and a private-sector-led large-scale private equity impact investment fund
The GFCR aims to promote sustainable ocean production
spur sustainable coastal development and ecotourism
forge circular economies and pollution management
and enable technologies for a sustainable future. The GFCR-funded MAR+Invest program is led by the Mesoamerican Reef Fund (MAR Fund) in partnership with regional actors New Ventures
and the Mexican Fund for the Conservation of Nature
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“The magnitude and extent of the heat stress is shocking,” said one marine scientist
A year after scientists warned the world was seeing its fourth mass coral bleaching event
rising ocean temperatures fuelled by greenhouse gas emissions have now devastated 84% of Earth’s coral reefs – with likely knock-on effects for about a third of all marine species and a billion people whose lives and livelihoods are directly affected by the health of the “rainforests of the sea”
Unusually warm ocean waters cause corals to expel algae that give the reefs their bright colour and deliver nutrients
supporting the immense biodiversity that is normally found within the reefs
“The magnitude and extent of the heat stress is shocking,” marine scientist Melanie McField
the founder of the Healthy Reefs for Healthy People initiative in the Caribbean
“Some reefs that had thus far escaped major heat stress and we thought to be somewhat resilient
succumbed to partial mortalities in 2024.”
“The fact that so many reef areas have been impacted," he said
“suggests that ocean warming has reached a level where there is no longer any safe harbour from coral bleaching and its ramifications.”
The current coral bleaching event began in January 2023
scientists were alarmed by an ocean heatwave off the coast of Florida that rapidly bleached the only living barrier reef in the continental United States
That event prompted NOAA to introduce a new coral bleaching alert scale from Level 1 — significant bleaching — to Level 5
at which point a reef is approaching mortality
Another ocean heatwave last year threatened Australia’s Great Barrier Reef
eight years after nearly half of the coral in some northern parts of the 1400-mile reef was killed by a mass bleaching event
But recent major bleaching events affecting specific reefs have not compared to the current widespread devastation in the world’s oceans
“With the ongoing bleaching it’s almost overwhelming the capacity of people to do the monitoring they need to do
global-scale coral bleaching event is still ongoing takes the world’s reefs into uncharted waters.”
The other three mass bleaching events on record occurred from 2014-17
with 68% of the world’s reefs affected; in 2010
a marine biologist at the Coral Reef Laboratory at the University of Southampton in England
emphasised that taking action to stop the heating of the world’s oceans could protect coral reefs
the marine species they provide habitats to
and the communities they support by protecting coastlines and providing fishing and tourism jobs
Julia Conley is a staff writer for Common Dreams
Ocean Reef Marina Breakwaters project from WA Limestone and Italia Stone Group Joint Venture has been nominated as the finalist for the 2024 WA Earth Award
DevelopmentWA engaged the JV to construct the breakwater and revetment structures with a combined length of 2km of seawall and 1km of revetment wall
The work scope included reuse of existing breakwater material; placement of geotextile
limestone core armour and granite armour; and excavation of dredging areas
Material supply was the biggest challenge for the project
with the management of importing 1.25 million tonnes of rock across more than 30 delivery sites impacting the delivery schedule
The 2024 WA Earth Awards will be held on Friday
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In the dead of the night a saw-wielding figure lurks in Ocean Reef – but the only victims that need to worry are the wooded kind with the potential to block ocean views
56 trees installed in four separate plantings at Tarolinta Park have been poisoned or cut by a brazen and unknown person or persons
Stuart Trott called the vandals of 12 Callistemon viminalis (Weeping Bottlebrush) and 8 Melaleuca quinquenervia (Broad-Leaved Paperbark) selfish.Credit: Claire Ottaviano
Residents fed up with the repetitive vandalism came out last week to discover someone had chopped 19 of 20 newly planted bottlebrush and paperbark trees – some directly in front of a recently installed sign aimed at deterring would-be vandals
It followed the vandalism of eight trees planted in May 2022 and vandalised a month later
13 trees planted in July 2022 and vandalised in August 2022 and 16 trees planted in August 2023 and vandalised in November 2023
Stuart Trott said the issue had been a persistent pain for the 10 years he had lived adjacent to the park
labelling the vandal “selfish” and “an idiot”
“The majority of people around here are dog owners or they have children who would like shade in the park,” he said
City of Joondalup Mayor Albert Jacob condemned the person responsible for cutting down new trees.Credit: Claire Ottaviano
“I think someone is doing it for pretty selfish reasons – probably someone who’s worried about their view.”
The City of Joondalup said each round of planting cost between $1500 and $2000
Unauthorised pruning or removal of trees is an offence under local laws with fines of up to $5000
Offenders may also be responsible for replacement and establishment costs
“It’s a crime at the end of the day,” Trott said
“Hopefully [the council] will persist and hopefully
whichever idiot who’s doing it will stop.”
expressed his disappointment and also speculated as to the motive of the alleged repeat offender
City of Joondalup Mayor Albert Jacob said if whoever was cutting down the trees to improve their views
“The trees that are already here are growing 10 to 20 meters
the trees they’re cutting down are paperbarks and bottle brushes which at most grow to five meters,” he said
Jacob said criticism connecting loss of ocean views to decreasing house values were invalid – as leafy green spaces were known to increase suburb desirability and value
He also said the city “unashamedly” had the most aggressive tree canopy target in WA
“The only way you end up with a leafy city is if a local government at a point in time says we’re going to aggressively plant trees and keep them here for the next generation.”
City of Joondalup deputy mayor Adrian Hill said the city had not received any complaints from residents about the planting of the trees
“People who vandalise trees are causing a loss of amenity and extra costs for our community by destroying community assets
and write to nearby land owners asking for support to identify and catch the culprits and report offending to police
The Morning Edition newsletter is our guide to the day’s most important and interesting stories, analysis and insights. Sign up here
In the dead of the night a saw-wielding figure lurks in Ocean Reef \\u2013 but the only victims that need to worry are the wooded kind with the potential to block ocean views
Residents fed up with the repetitive vandalism came out last week to discover someone had chopped 19 of 20 newly planted bottlebrush and paperbark trees \\u2013 some directly in front of a recently installed sign aimed at deterring would-be vandals
labelling the vandal \\u201Cselfish\\u201D and \\u201Can idiot\\u201D
\\u201CThe majority of people around here are dog owners or they have children who would like shade in the park,\\u201D he said
\\u201CI think someone is doing it for pretty selfish reasons \\u2013 probably someone who\\u2019s worried about their view.\\u201D
\\u201CIt\\u2019s a crime at the end of the day,\\u201D Trott said
\\u201CIt is taxpayer money getting wasted
\\u201CHopefully [the council] will persist and hopefully
whichever idiot who\\u2019s doing it will stop.\\u201D
\\u201CI\\u2019m assuming people who have a view
I\\u2019m going to lose my ocean view,\\u201D he said
it\\u2019s not their park and when you buy here
you buy knowing there\\u2019s a park in front.\\u201D
\\u201CThe trees that are already here are growing 10 to 20 meters
the trees they\\u2019re cutting down are paperbarks and bottle brushes which at most grow to five meters,\\u201D he said
Jacob said criticism connecting loss of ocean views to decreasing house values were invalid \\u2013 as leafy green spaces were known to increase suburb desirability and value
He also said the city \\u201Cunashamedly\\u201D had the most aggressive tree canopy target in WA
\\u201CWe are determined to plant [trees] ..
the council is united on it,\\u201D he said
\\u201CThe only way you end up with a leafy city is if a local government at a point in time says we\\u2019re going to aggressively plant trees and keep them here for the next generation.\\u201D
\\u201CPeople who vandalise trees are causing a loss of amenity and extra costs for our community by destroying community assets
The Morning Edition newsletter is our guide to the day\\u2019s most important and interesting stories
Metrics details
Coral reef restoration can reduce the wave-driven flooding for coastal communities
this protection has yet to be assessed in terms of the reduced risk of flood-driven environmental contamination
Here we provide the first high-resolution valuation of the reduction of flood-related land-based environmental pollution provided by potential coral reef restoration
Along Florida’s 460 km-long coral reef-fringed coastline
coral reef restoration could reduce the risk of sewage and petrochemical contamination by preventing the flooding of petroleum storage tank systems (-9%)
onsite sewage treatment and disposal systems (-4%)
The present value of critical infrastructure protection and contamination prevention benefits provided by coral reef restoration is $3,413,503
10,404 GPD of wastewater treatment capacity
demonstrating that coral reef restoration can provide environmental risk reduction and previously undocumented additional socioeconomic benefits
coastal flood hazards are increasing and thus so is the potential for storm-driven contamination
assessing the impact of flooding and the resulting environmental contamination on such communities is an environmental justice issue
and WWTPs that could be damaged and potentially cause environmental contamination
The CIE protection and contamination prevention (CPCP) benefits are defined as damages to CIEs and potential resulting environmental contamination that can be adverted with coral reef restoration compared to the current state of coral reefs
we advance the precision of the computation of economic damages and economic benefits
provided by coral reef restoration by presenting results as probability distributions
to provide a holistic presentation of flood contamination risk
The restoration of coral reefs can avert economic damages that otherwise can occur when CIEs are flooded and subsequently damaged during wave-driven flooding events
Damages are defined as those to CIEs that limit their functionality and operability and cause related potential environmental contamination that require either repair or replacement of the element itself
as well as potential environmental remediation and cleanup of the surrounding area
Associated with these damages are the costs of repair and/or replacement of CIEs and environmental remediation measures
and therefore do not include facilities with other industrial hazardous waste and thus are a conservative underestimation of the total possible contamination
Coral reef restoration considered here consists of a solid structure with outplanted coral on top and total elevation increase of 1.25 m and width of 5 m in cross-shore direction (refer to Methods for details) is projected to reduce the number of pSTs, OSTDSs, and WWTPs (Fig. 1) at flood risk.
with above ground in yellow and underground in red
c Onsite sewage treatment and disposal systems
The dark blue areas indicate the areas that are in a flood hazard zone for current coral reefs and the light blue areas indicate the reduced flood zones with coral reef restoration
Orange areas represent the spatial extent of wastewater treatment plants and red areas indicate properties containing an onsite sewage treatment and disposal system
Coral reef restoration is projected to reduce the size of coastal floodplains
reducing the flooding of properties containing pSTs
and WWTPs and the resulting environmental contamination
e Expected annual damages with regards to the number of critical infrastructure elements (label on top of columns) and percentage averted (percentage in green columns)
f Expected annual damages with regards to the economic damages (labels on top of the columns) and percentage adverted (percentage in green columns)
The dark gray bars indicate the damages projected for current coral reefs and the green bars indicate damages for restored coral reefs
Coral reef restoration can reduce the number of flooded pSTs
and WWTPs and related economic damages per storm return interval and thus annual damages
The critical infrastructure element (CIE) protection and contamination prevention (CPCP) benefits of coral reef restoration are dependent on the storm return interval and vary by type of critical infrastructure
Because coral reef restoration is projected to reduce the number of flooded CIEs
it will likely also reduce the number of newly contaminated sites
By reducing the number of flooded CIEs, coral reef restoration is projected to decrease the volume of petroleum product and sewage capacity at risk for a given storm. For the 100-year floodplain, 59,300 U.S. gal of petrochemicals and a sewage capacity of 7500 U.S. gal per day (GPD) (Fig. 3) are projected to be protected from flooding with restored coral reefs in Florida.
a Relation between the volume of petroleum product at flood risk and the flooded area for different storm return intervals
The dashed circles indicate the values that correspond to a particular storm return interval (10-year
b Relation between the capacity of sewage at flood risk and the flooded area for different storm return intervals
c Expected annual damages (label to the right of bars) and percentage avoided (percentage in green bars) with regards to the volume of petroleum products stored and the capacity of sewage treated in zones with flood risk
Dark gray bars indicate the volume of contaminants stored in floodplains based on current coral reefs and green bars represent those in floodplains with restored coral reefs
Coral reef restoration is forecasted to reduce the volume of gasoline
and the capacity of sewage at flood risk during wave-driven coastal flooding events and thus is projected to lessen the extent of environmental contamination by those pollutants
gal (−3.0%) of petroleum products and a sewage capacity of 7,737 GPD (−0.5%) from WWTPs and 2,667 GPD (−3.8%) of sewage from OSTDSs are projected to be protected from flooding by restored coral reefs annually
These disaggregate into projected annual flood protection of 9.7% (30,954 U.S
gal) of other chemical substances (see Methods for details)
Due to the location of pSTs containing aviation fuels (82,522 U.S
annually none of these are forecasted to be protected with coral reef restoration
With coral reef restoration projected to reduce the volume of petroleum-product and sewage capacity at flood risk
it will reduce the overall environmental burden and necessity for cleanup measures for a given region
Damages refer to physical damage to critical infrastructure elements and the resulting environmental contamination with petrochemicals and/or sewage
Economic damages include costs for repair and/or replacement of those critical infrastructure elements
as well as costs for environmental remediation and cleanup
a Histogram of the present value of damages
b Histogram of the present value of CPCP benefits
c Distribution of the PV(D) per county for current coral reefs
d Distribution of the PV(B) provided by restored coral reefs per county
the blue horizontal lines indicate the 25 and 75% quantiles
the red horizontal line represents the median
and whiskers display the minimum and maximum values; extreme values are denoted by points
a discount rate of 7% and 30-year lifetime were assumed
Expected annual CPCP benefits for pSTs are US$110,000 (7%), for OSTDS US$11,000 (4%), and for WWTPs US$160,000 (14%). For areas in the 100-year floodplain of coral-fringed Florida, reef restoration can provide mean CPCP benefits to CIE of US$553,005 ± US$377,715 (7.2%) (Supplementary Fig. 2)
Coral reef restoration is thus projected to reduce the financial burden for post-disaster measures for reconstruction of the functionality and operability of CIEs and environmental remediation for a given region
Florida has 460 km of coral reef-fringed coastline
of which 226 km (49.1%) are forecasted to experience CIE and potential flood contamination damages over the next 30 years due to wave-driven coastal flooding events if reefs remain unrestored (“current reefs”)
Coral reef restoration is estimated to protect CIEs along 81 km
and 35.8% of coastline for which damages are projected
Depending on the section of coastline considered
restored coral reefs are projected to offer mean present values of CPCP benefits ranging from US$0 to US$1,560,000/km
with a mean ± standard deviation of US$7,421 ± US$83,286
coastal protection benefits can range from US$0/km to US$900,000/km
with a mean ± standard deviation of US$4,620/km ± US$44,189/km (6.0%)
Expected annual CPCP benefits are forecasted to range from US$0 to US$493,200/km
with a mean ± standard deviation of US$2,254/km ± US$27,228/km
with a mean ± standard deviation of 8.1 ± 22.5%
are projected to be averted by restored coral reefs
although coral reef restoration might not avert damages for some sections of Florida’s reef-fringed coastline
it is projected to reduce the flood-related damages and contamination for some coastal segments almost entirely
Coral reef restoration can protect critical infrastructure from damage and coastal communities from environmental contamination resulting from wave-driven coastal flooding events
Our results demonstrate that coral reef restoration in Florida could protect pSTs
OSTDSs and WWTPs from flood-related damages and spills that are equivalent to expected annual economic protection benefits of US$281,435 (2022 US$); as noted in the Methods
as we did not consider smaller fixed or mobile sources
and we used conservative radii of the polluted environment
With regards to total flood-caused contamination in Florida
such as facilities with industrial or hazardous waste
a Expected annual economic damages per 1-km coastal segment forecasted for current coral reefs
b Expected annual CPCP benefits restored coral reefs are projected to provide per 1-km coastal segment
c Mean present value of damages to critical infrastructure elements for current coral reefs
d Mean present value of CPCP benefits restored coral reefs could provide per 1-km coastal segment
Coral reef restoration can substantially reduce the coastal hazard risk of flood damages to CIEs and subsequent contamination; however
the damages and protection benefits are highly spatially variable due to the nature of the coral reefs and distribution of infrastructure potentially causing contamination
if restored coral reefs can protect the flooding of CIEs and other contaminant sources
it can reduce the chances that new sites of contamination develop
coral reef restoration would also reduce the flood hazard for sites of known
existing contamination for reef-fringed tropical coastlines
it could reduce the economic and environmental burden for coastal communities associated with post-disaster recovery and environmental remediation
Further studies on additional contaminant sources
and related times of exposure to flooding are necessary to assess further flood contamination risks
By averting flood damages to CIEs and avoiding flood-related environmental contamination for various areas and different functions within coastal communities
coral reef restoration can reduce the short- and long-term human health hazard
the CPCP benefits quantified in this study are but a small portion of the expected benefits from reef restoration
This method of Monte Carlo simulations is applied here for the first time to assess CPCP benefits restored coral reefs can provide
coral reef restoration could reduce the future financial and environmental burden arising from environmental cleanup
Coral reef restoration therefore could contribute to the protection of common goods and peoples from flood-related environmental contamination
and it could thus be a measure to improve environmental justice for underserved communities
Our study area consists of the coastal areas of the counties Martin
Middle and Lower Keys) in Monroe County in Florida
and a second dataset with information on tank contents was provided directly by FDEP
We chose to round down to 4 bedrooms to conduct a conservative estimate
Our study represents a conservative approach by assessing the flood contamination risk for pSTs
OSTDSs and WWTPs that are officially registered with the Florida Department of Environmental Protection
We also assumed a conservative zone of impact of environmental contamination of CIE damage
CPCP benefits provided by coral reef restoration for petrochemical exposure could even be higher if further contamination sources of anchored nature (i.e.
storage tanks for emergency generators below the threshold) or mobile nature (i.e.
and if the radius of the assumed polluted environment is assumed to be larger
The restored coral reef scenario describes a restoration scenario that consists of a solid structure with outplanted live coral top with total vertical height increase of 1.25 m and a cross-shore width of 5.0 m that were situated in water depths between 2 and 7 m on continuous coral/hardbottom habitat and located at the closest point to shore
There are two ways how this could be achieved: (a) either outplanting of tall (mature) live coral
(b) a structural or “gray” restoration with a concrete or metal base structure and juvenile corals rescued from elsewhere or grown in nurseries outplanted on top
Such a base structure in combination with the outplanting of live coral is often referred to as a “hybrid” restoration
(2012b) modeled each of the reef scenarios (current reefs
a theoretical reef restoration location was determined based on the bathymetry of the seafloor for depths between 2 and 7 m
and WWTPs affected and protected from flooding with a quantitative geospatial analysis in ArcGIS Pro
All locations of CIEs within a distance of 500 m of the largest floodplain (500-year storm return interval
current reefs) were individually verified with Google Maps (satellite imagery)
and ArcGIS Pro Imagery Hybrid map to account for spatial inaccuracies
A detailed description of the procedure can be found in the following three subsections
The location of each individual petroleum storage tank within a property corresponding to an address was verified with Google Maps
permit documents and annual inspection reports found at respective links in the FDEP datasets
pSTs located higher than the second story of a building were excluded
since we assumed that flood waters will not reach these storage tank systems
The point layer containing the location of pSTs was intersected with each of the eight floodplain layers
the tool spatial join with a radius of 15 m was selected to account for the spatial extent of a storage tank and floodplain uncertainties
The location of OSTDSs as provided in the datasets was at the street level
we intersected the polygon layer containing polygons of properties with OSTDSs with each of the floodplains to determine the projected flooded area of the properties
the areas of the flooded space of each property containing an OSTDS was measured for each of the flood scenarios
the spatial ratio \(\alpha\) of flooded property area to total property area was calculated and a spatial cut-off ratio of 20% was used
it was defined that the OSTDS on that property was flooded
If less than 20% of the property area was flooded
it was defined that the OSTDS was not flooded
We justify a spatial ratio \(\alpha\) of 20%
because on average only a limited area within a property is suitable for an OSTDS to be constructed as there are spatial requirements (open space free of trees
no other built structures on top that could damage the absorption field)
Since OSTDSs considered consist of the basic modules of septic tank
by the physical principle of communicating vessels we assume that if one part of an OSTDS is flooded and flood water enters the system somewhere
or even the entire system can become damaged and sewage spills can occur somewhere in the system
we considered the use of a ratio \(\alpha\) = 0.2 as the cut-off value
which means one fifth of the property being flooded
the state of a particular OSTDS (flooded/not flooded) was determined
The number of OSTDSs flooded for a given scenario was determined by counting the number of properties containing an OSTDS with a spatial ratio \(\alpha \ge\) 20% for a given flood scenario
The addresses of WWTPs were provided as a point feature class
We verified the location of the property corresponding to an address with Google Satellite Images
We then further refined the WWTP’s spatial extent within a property with information found in official permits
A respective link to a FDEP database to access these documents was found for every entry of the FDEP dataset
The WWTP polygon layer was intersected with each of the floodplains and the area of the flooded area within the WWTP was computed
the spatial ratio \(\alpha\) of flooded area to total area of the WWTP was calculated
a spatial cut-off ratio of 20% was used to determine the state (flooded/ not flooded) of a WWTP for a given flood scenario
and WWTPs protected from coastal flooding with restored coral reefs was computed as the difference between the number of flooded pSTs for the scenario with current reefs for a given storm return interval
and the number of pSTs with restored reefs for the same storm return interval:
with N being the number of critical infrastructure elements and m being the type of critical infrastructure element (pST
A SLOSH simulation is a computational model to simulate storm surges
we identified related damage probabilities based on our results found in the literature search and then allocated the estimated damage probabilities to our different possible events in our decision trees
Decision trees for pST and OSTDS damage can be found in Supplemental section are not described here in detail due to a lack of space to include in manuscript
All found monetary values were converted to 2022 US$
For the estimation of economic flood damages and the projection of economic flood protection benefits restored coral reefs can provide, we used Monte Carlo simulations with 1000 iterations (Supplementary Fig. 11)
We used two different types of Monte Carlo algorithms
one for the estimation of the present values of damages and CPCP benefits at different scales (per kilometer of coastline
total study area) and one other type for the assessment of damages and benefits projected per storm return interval (10-year
The latter one becomes also relevant for the computation of expected annual damages and benefits (refer to paragraph “Expected annual damages and benefits“ below)
The 460 km long coastline was divided into 1 km wide coastal segments
The algorithm to determine the present values per county and study area is described here
per year (ranging for year 0 to year T (maturity))
we randomly chose a storm of a given storm return interval (10-year
500-year; no storm) and corresponding probability of occurrence (1/10; 1/50; 1/100; 1/500; 0.868)
every coastal segment of length 1 km along the coast can be affected
For each pST and OSTDS within the flooded region
we chose a random respective damage scenario based on previously determined damage probabilities
and we randomly chose a value for occurring costs based on previously modeled PERT distributions
For WWTPs we used previously determined economic losses based on damage degrees
We then took the occurred damages for each individual CIE and summed up the economic damages per regional scale (per kilometer of coastline; per county; per study area)
We repeated this procedure for each year from t = 0 to maturity t = T and discounted each year with a discount rate (see formula below)
We then computed the present value of damages \({PV}{\left(D\right)}_{s,c,i}\) and the present value of CIE protection and contamination prevention (CPCP) benefits \(PV{\left(B\right)}_{s,i}\) by summing up over the damages
Hereby s is the regional scale (per coastal segment
c is the coral reef restoration scenario (current reefs
t is the time in years from year 0 to T (time of maturity)
We used a maturity T of 30 years and a discount rate r of 7% as it is commonly used by FEMA and the U.S
federal discount rate was reduced from 7 to 3.1% in 2024
thus our results can be considered conservative
The mean present value of economic damages \({PV}{\left(D\right)}_{s,c}\) describes the flood damages to critical infrastructure that are estimated to occur over a specified period of time
a particular state of coral reef and assumed discount rate
The mean present value of economic CIE protection and contamination prevention (CPCP) benefits (\({PV}{\left(B\right)}_{s}\)) describes the amount of economic damages \({PV}{\left(D\right)}_{s,c}\) over a given time period for a specified region that can be prevented from occurring with a restored coral reef
compared to the present-day state of a coral reef (“current reefs”)
The \({PV}{\left(D\right)}_{s,c,i}\) and \({PV}{\left(B\right)}_{s,i}\) were computed for three different scales: per coastal segment of length 1 km
We repeated this computation 1000 times (1000 iterations; for clarification: damage scenarios and storm return intervals were randomly chosen based on damage probabilities for each iteration)
and then computed the mean and standard deviation over these 1000 iterations to determine the mean \({PV}{\left(D\right)}_{s,c}\)
and corresponding standard deviations for different spatial ranges and coral reef restoration scenarios
All mentioned monetary values were converted
i representing the respective storm return interval (10-year
1/ Ti is the respective annual exceedance probability (1/10
Di represent projected mean damages per respective storm return interval
For expected annual CPCP benefits coral reef restoration can provide
we computed the difference in predicted mean flood losses between a state with present-day coral reefs and a state with restored coral reefs:
Both expected annual damages and expected annual CPCP benefits were further computed for four additional types of parameters: (1.1) the number of CIE projected to be flooded; (1.2) the number of CIE projected to be protected from flooding; (2.1) the estimated volumes of petroleum products and the capacity of wastewater treatment at flood risk; (2.2) the estimated volumes of petroleum products and the capacity of wastewater treatment projected to be protected from flooding
In our model we assumed that floodplains remain constant over a lifetime T = 30 years
This means we assumed the state of current and restored coral reefs also remains constant
and thus there is no degradation of coral reefs over time
future continuous coral reef degradation can occur if coral reefs are not restored and if the threats that killed the reefs in the first place are not mitigated
and this would change the floodplain corresponding to the state of current reefs for a given year
climate change impacts the severity of storm events
and a storm event of certain magnitude and annual exceedance probability can be classified as an event with lower annual exceedance probability (10-year storm can become 5-year storm in the future)
There are 6 CIE factors that affect the CPCP benefits per length of coastline: (1) the number of CIEs per coastal segment
which is related to the population density and type of CIE technology of a municipality (i.e.
OSTDS); (2) location of a CIE relative to the wave-driven floodplains; (3) number of storm return intervals for which a CIE is protected
as this affects the present value of CPCP benefits and expected CPCP benefits; (4) type of CIE protected
as there are different repair and/or replacement costs for different types of CIEs; (5) size of CIE affected
as the costs for reparation/replacement of pSTs and WWTPs depend on size; and (6) damage probabilities for a flooded CIE
the higher the number of CIEs protected from flooding by reef restoration
the higher the number of storm-return intervals for which a CIE is protected
the larger the volume of pSTs or capacity of WWTPs
and the higher the damage probability for a CIE
the higher the CPCP benefits per coastal segment on the benefits side of the benefit-cost-analysis
We further assumed for our Monte Carlo simulation that either no storm or one storm of a random storm return interval can occur per year
there have been years with 2 storm events per year in same location
This would imply that annual damages could be higher because the sum of storm damages of two events per year are likely to be higher than only for one
Since our intention was to conduct a conservative approach
we are aware that the extent of storms can cause storm surges of different spatial extent
We have experimented with different spatial extents of storms
but instead of presenting the results from multiple models with different assumptions
we focus on the results from the most transparent assumption
Our results of the present value of damages and the present value of CPCP benefits show a high standard deviation
because the storm of certain storm return intervals are randomly selected based on given probabilities
If one compares one run of a Monte Carlo simulation in which one 500-year and one 100-year storm occurs
and another run in which only two 10-year storms occur
it can be seen that the sum of damages differs
Also relevant is the year the storm of a given storm return interval occurs
this result visualizes very well the reality: if no storm event occurs
the coastal protection function of a coral reef is not required
if a storm event with coastal flooding occurs
damages occur within the short time frame of a couple hours to days
and economic damages can be several million to tens of millions of dollars
the coastal protection function of a coral reef is strongly beneficial
Further information on research design is available in the Nature Portfolio Reporting Summary linked to this article
The developed Matlab code for the Monte Carlo simulation will be provided upon request
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Geological Survey (USGS) Coastal and Marine Hazards and Resources Program’s Coral Reef Project as part of an effort in the United States and its trust territories to better understand the effect of geologic and oceanographic processes on coral reef systems
through the Coastal and Marine Hazards and Resources Program funding from the 2017 Hurricanes and Wildfire Supplemental
We want to thank Christopher Williams (Florida Department of Environmental Protection) and Kristen Alkins (USGS) for the provision of geospatial data
Patrick Barnard (USGS) contributed numerous excellent suggestions and a timely review of our work
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All corals require very salty water to survive—from 32 to 42 parts per thousand—restricting them to coastal and open ocean areas
different types of coral communities are typically located in parts of the ocean based on their light requirements
The red dots on the map represent the locations of reef building stony corals around the world. The majority of reef-building stony corals are found in shallow tropical and subtropical waters ranging from 35N to 35S latitude. View a large map of where reef building corals are found.
Shallow water stony corals are typically found in areas that receive a lot of light and warm water
Many grow the best in water temperatures between 23° and 29° C (73.4° and 84.2° F)
but some can tolerate temperatures as high as 40° C (104° F) for short periods
These corals’ requirement for high light also explains why most reef-building species are restricted to the region in the ocean where light penetrates to a depth of approximately 30 meters (98.4 feet)
but its intensity dwindles as it passes through the depths of the sea
Yet even the ocean’s dim middle reaches—the mesophotic zone (and its deepest
or deep benthic zone)—host an abundance of life
Mesophotic corals (meso meaning middle and photic meaning light) are so named because they have lower light requirements than shallow corals
enough sunlight still reaches the mesophotic zone to support light-dependent coral species
Sometimes healthy deep sea corals take on a stark white appearance. Learn more and view a larger image.
Mesophotic coral reefs are usually understudied because they are too deep to reach with regular scuba gear and often too shallow for submarine expeditions
with the increasing safety and accessibility of technical diving and remotely operated vehicle technologies
larger areas of mesophotic coral communities are being explored
scientists have discovered there are reefs in parts of the deep sea
they grow much slower than their shallow water counterparts
How to cite this article
David Shiffman has consulted for many environmental non-profit groups including the Ocean Conservancy
as well as fishing industry groups and fisheries managment agencies
Arizona State University provides funding as a member of The Conversation US
View all partners
The single greatest threat to the diversity of life in our oceans over the past 50 years, more than climate change or plastic pollution
In much of the ocean, there is little to no regulation or oversight of commercial fishing or other human activities. That’s part of the reason about a tenth of marine plant and animal species are considered threatened or at risk
It’s also why countries around the world have been creating marine protected areas
These protected areas, covering over 11.6 million square miles (30 million square kilometers) in 16,000 locations, offer refuge away from human activities for a wide variety of living creatures, from corals to sea turtles and whales. They give fish stocks a place to thrive, and those fish spread out into the surrounding waters
which helps fishing industries and local economies
In the U.S., however, marine protection is being dismantled by President Donald Trump
I’m a marine biologist and scuba diver, and it’s no accident that all my favorite dive sites are within marine protected areas. I’ve found what scientific studies from across the world show: Protected areas have much healthier marine life populations and healthier ecosystems
The Pacific Island Heritage National Marine Monument
marine mammals and birds rarely found anywhere else
It is home to protected and endangered species, including turtles, whales and Hawaiian monk seals. Palmyra Atoll and Kingman Reef, both within the area, are considered among the most pristine coral reefs in the world
each providing habitats for a wide range of fish and other species
These marine species are able to thrive there and spread out into the surrounding waters because their habitats have been protected
is now reopening much of the marine protected area to industrial-scale fishing
When too many fish are killed and too few young fish are left to replace them
and this has become a growing problem around the world
In 1974, about 10% of the world’s fish stocks were overfished. By 2021, that number had risen to 37.7%, according to the United Nations Food and Agriculture Organization’s annual State of Fisheries and Aquaculture Report
Modern industrial-scale fishing practices can also harm other species
Without regulations or protected areas, fishing can turn into a competitive free-for-all that can deplete fish stocks
Marine protected areas are designed to safeguard parts of the ocean from human impacts
including offshore oil and gas extraction and industrial fishing practices
Studies have found that these areas can produce many benefits for both marine life and fishermen by allowing overfished species to recover and ensuring their health for the future
A decade after Mexico established the Cabo Pulmo protected area, for example, fish biomass increased by nearly 500%
Successful marine protected areas tend to have healthier habitats, more fish, more species of fish, and bigger fish than otherwise-similar unprotected areas. Studies have found the average size of organisms to be 28% bigger in these areas than in fished areas with no protections
How many babies a fish has is directly related to the size of the mother
All of this helps create jobs through ecotourism and support local fishing communities outside the marine protected area
Marine protected areas also have a “spillover effect” – the offspring of healthy fish populations that spawn inside these areas often spread beyond them
helping fish populations outside the boundaries thrive as well
the fishing industry benefits from a continuing supply
Claims by the Trump administration that marine protected areas are a heavy-handed restriction on the U.S
these refuges for sea life can instead help local economies and the industry by allowing fish populations to thrive
coral reefs and the health of fishing itself
scientists like me recommend creating more marine protected areas to help species thrive
Driving Global Action to Protect Coral Reef with Innovative Financing
2025 /PRNewswire/ -- Saudi Arabia has officially assumed the Secretariat of the International Coral Reef Initiative (ICRI) for its 14th term
marking a significant milestone in global coral reef conservation
ICRI represents 102 members including 45 countries that are custodians of 75% of the world's coral reefs
The Kingdom's leadership for this three-year term was confirmed by ICRI members during the 38th General Meeting in September 2024
Saudi Arabia will lead this historic role through the General Organization for the Conservation of Coral Reefs and Turtles in the Red Sea (SHAMS)
The virtual handover ceremony featured distinguished attendees
the UN Secretary-General's Special Envoy for the Ocean
Department of State and other distinguished entities
which sustain 25% of the world's marine biodiversity
contribute an estimated US$9.9 trillion annually in goods and services
highlighting their immense ecological and economic value
ICRI members are working under Saudi Arabia's leadership to develop the 2025–2027 Action Plan
The plan aims to expand membership to include 90% of the world's coral reefs
integrating resilient reef management into global policies and enhancing national biodiversity strategies
Key priorities include boosting the blue economy
advancing reef monitoring with innovative technologies
and utilizing insights from the upcoming "Status of Coral Reefs of the World: 2025" report
Other notable initiatives include the launch of ICRI's Youth Strategy
strengthening collaboration in the Red Sea
and raising global awareness through major events such as the UN Ocean Conference
This milestone underscores Saudi Arabia's commitment to environmental stewardship
aligning with Vision 2030's ambitious sustainability goals and economic diversification strategy
It also complements the recently launched National Strategy for Red Sea Sustainability
which reinforces the Kingdom's dedication to conserving the Red Sea's unique marine ecosystems and creating a sustainable blue economy
emphasized the significance of this role: "Saudi Arabia's role as ICRI Secretariat underscores our unwavering commitment to a sustainable future for coral reefs worldwide
We are deeply grateful to ICRI members for their trust and recognition in selecting Saudi Arabia to lead this critical global initiative
we aim to set new benchmarks in coral reef conservation
and collaboration to drive both national and international initiatives
Our goal is to protect these vital ecosystems
ensuring their resilience for future generations while maintaining their invaluable contributions to the global economy."
The General Organization for the Conservation of Coral Reefs and Turtles in the Red Sea (SHAMS) is the governmental body mandated to regulate
and ensure the sustainable management of Saudi Arabia's exceptional and one of the world's most resilient coral reefs and sea turtle ecosystems in the Red Sea
implements large-scale restoration projects
and develops sustainable management frameworks to safeguard these critical ecosystems
For more visit: http://shams.gov.sa
The International Coral Reef Initiative (ICRI) is a global partnership between Nations and organisations that strives to preserve coral reefs and related ecosystems around the world
The Initiative was founded in 1994 and has since grown to a network of 102 members
including 45 countries who represent over 75% of the world's coral reefs
For more visit: www.icriforum.org
SOURCE General Organization for the Conservation of Coral Reefs and Turtles in the Red Sea (SHAMS)
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The coral reefs that dot Colombia's sprawling Sea Flower Biosphere Reserve are among the most vibrant in the Caribbean
invasive species and climate change are decimating these undersea cities
threatening marine life and the livelihoods of thousands of people
a novel funding mechanism is helping relieve some of those stressors.
The Global Fund for Coral Reefs
a multi-partner trust fund supported by the United Nations
is providing grants and soft loans to small businesses that operate within the reserve
The funding is backing several reef-friendly ventures
The financing is part of a growing effort by governments and philanthropies to use seed money to jumpstart private investments in conservation
with the support of the Global Environment Facility (GEF) and the World Bank
the Republic of Seychelles launched the world’s first sovereign blue bond in 2018 to support sustainable marine and fisheries projects
demonstrating the potential for countries to harness capital markets for financing the conservation
restoration and sustainable use of marine resources.
“If we’re to achieve the targets of the Global Biodiversity Framework
nations need to massively scale up the amount of resources they are dedicating to nature,” said Sinikinesh Beyene Jimma
interim Head of Marine and Freshwater Branch from the United Nations Environment Programme (UNEP)
hold the key to generating that capital.”
The protection of marine spaces is traditionally funded by governments
often because businesses view investments in sustainability as risky
Blended finance uses a combination of guarantees
concessional loans and impact bonds to reduce private investors’ exposure
“It gives businesses the confidence they need to invest in sustainability
most businesses will find these investments make financial sense
even without government and philanthropic support,” Jimma said.
This week, representatives from 196 nations are in Cali, Colombia for the UN Biodiversity Conference
where negotiators are focusing on how to round up more financing for biodiversity
Some are looking at the Global Fund for Coral Reefs as a model.
Launched in 2020, the GFCR has raised more than US$90 million in grant funds and close to US$150 million in private investments for what it calls “coral-reef-positive” businesses around the world. This money has helped to support everything from ecotourism to sustainable aquaculture to seaweed farming
The GFCR aims to support over 400 reef-positive businesses and directly create more than 30,000 reef-positive jobs by 2030
In the UNESCO-designated Seaflower Biosphere Reserve
home to 77 per cent of Colombia’s coral reefs
the fund is projected to raise more than US$16 million in private investment
and support more than 65,000 community members with increased resilience across Colombia by 2030
the programme in Colombia aims to increase live coral cover by 4 per cent and protect 825 square kilometers of reefs
It is also hoping to rein in the spread of algae
Experts expect this work to lead to an increase in fish
which will improve food security for local communities
and raise income from fishing and tourism by about 40 per cent.
The fund’s efforts come on the heels of 18 months of unprecedented ocean heat that is spelling disaster for the world’s coral reefs. The United States of America’s National Oceanic and Atmospheric Administration (NOAA) says more than 70 per cent of corals around the world have experienced heat stress that can trigger bleaching
many of whom live in the world’s least-developed countries
Yet these vital ecosystems continue to be degraded
the Global Fund for Coral Reefs launched a US$3 million
seven-year project focusing on the Bird’s Head Seascape and Pulau Sumba — an epicentre of marine biodiversity.
allowing Indonesia to redirect debt payments towards coral reef conservation and showcasing the potential of innovative financial approaches.
Projects like these cannot stop ocean warming and coral bleaching being wrought by climate change
But they can reduce local stressors on coral reefs and give them a better chance of recovery and survival.
“What we’re doing is giving corals a fighting chance,” said Sinikinesh Beyene Jimma from UNEP
“That’s vital for protecting the stunning diversity of life in the ocean
it’s pivotal for the futures of millions of people who rely on marine ecosystems for their livelihoods.”
The Kunming-Montreal Global Biodiversity Framework
The planet is experiencing a dangerous decline in nature. One million species are threatened with extinction, soil health is declining, and water sources are less predictable. The Kunming-Montreal Global Biodiversity Framework sets out global targets to halt and reverse nature loss by 2030
and close the financial gap for nature.
The Global Fund for Coral Reefs (GFCR) was established to accelerate urgent investment and action to enhance the resilience of coastal reef ecosystems
The GFCR comprises two major financial vehicles: a UN-led Grant Fund and a private-sector-led large-scale private equity impact Investment Fund
and enable technologies for a sustainable future
ABC Newsurgent briefing on the state of Ningaloo.
Scientists like Dr Quigley would like to see him and other government officials communicating more with the public on the scope of what's happening in WA.
"We want to see this communicated to the public," she said.
"People have a right to know what's happening in their marine protected areas, in their World Heritage sites."
Paul Gamblin, the director of the conservation group Protect Ningaloo, said there should have been more communication during the build-up of the heatwave weeks ago.
"The government should explain to the community why these marine heatwaves are occurring now since they are very much a recent phenomenon," he said
Back in Exmouth, boat skipper Mr Kitson says it could be confronting to see all the impacts happening to the Ningaloo Reef, but the most important thing is that people still come and connect with the place for themselves.
"I did a tour this week and had snorkellers in the water and it was the most fantastic thing they've ever done," he said.
"Compared to most reefs in the world it's still among the best. It's important people come and learn and see the changes and connect with the place.
The Anohni and the Johnsons singer is collaborating with marine scientists for two special shows at Sydney’s Vivid festival that will show the reef’s plight
“I feel like I’m going to Auschwitz,” she says nervously
I’m so excited to go because the landscape is so beautiful
and I know there’s going to be so much that’s gorgeous
In a week, the British-born, New York-based avant garde singer of Anohni and the Johnsons is flying to Lizard Island
Its luxury villas and bluest of blue waters are a stark contrast to the grim nature of Anohni’s assignment: documenting the current state of the world’s biggest coral reef
“Where are the ceremonies fit for the purpose of naming and commemorating the times that we’re living through?” she asks. “To see the Great Barrier Reef fall, that’s 10,000 9/11s.”
“People can’t really imagine something on that scale dying,” she says.
a production company that specialises in underwater and conservation films
Anohni will be directing the scuba team from the surface in her snorkel
“I can’t believe I’m doing it,” she laughs
Just as a dying star glows more brightly before it goes dark
coral look even more beautiful in distress
Fluorescing – a phenomenon when corals release a garish pigment into their flesh as a sign of heat stress – is deceptively spectacular; and bleaching – when corals expel the photosynthetic algae that give them colour in response to warmer ocean temperatures – turns them a dazzling white
View image in fullscreenBleached and dead coral around Lizard Island on the Great Barrier Reef in April last year
Photograph: David Gray/AFP/Getty Images“It is like when someone’s dying
sometimes they show the gold of the soul,” Anohni says
“They throw their life force into a final expression
That’s what coral bleaching is … she’s saying goodbye.” She describes a conversation she had with a scientist who went out to visit a dead reef with a group of Danish students
“and they were all saying it was the most beautiful thing in the world
because they didn’t even know what they were looking at was a bunch of skeletons”
Anohni has long been singing about the climate crisis, sneaking this bitter pill into her beautiful, otherworldly songs. “I need another world,” she sang sorrowfully on 2009’s Another World. “This one’s nearly gone.” On 4 Degrees
released as world leaders met for the 2015 Paris climate conference
she sang her grim vision of the future: “I wanna hear the dogs crying for water / I wanna see the fish go belly-up in the sea / And all those lemurs and all those tiny creatures / I wanna see them burn
She has grown used to being seen “as a kind of a Cassandra on the sidelines”; the prophet doomed to be ignored
she is “so grateful” for being alienated in a way – as a trans artist
as a climate activist – “because when you have an outsider status
you have an opportunity to see the forest for the trees”
It Must Change by Anohni and the JohnsonsAnohni has a special connection to Australia: in 2013
she was invited to visit the Martu people of Parnngurr
When she asked one Martu woman where they believed people went after death: “She just looked at me like I was an idiot and said
from a British and Irish Catholic background
peaceful acceptance of this animist reality,” she says
“I was raised in a society where they believed that only humans had souls and that this place was basically just a suffering ground where we had to mind our Ps and Qs
“I screamed at those fucking wankers, and made a fucking fool of myself,” she says, smiling, “and I was torn a new arsehole in the Murdoch press.” But at the same time, she was inundated with messages of support from all over the country. “I was proud of the chance to be of service to Australians,” she says.
There is no hope of reefs surviving to even mid-century in any form that we now recognise.”
“Australia is pioneering in this oeuvre of environmental feeling,” Anohni says
“It’s could be something to do with the Australian temperament
very cruel in that regard – any expression of emotion is grounds for exclusion from any conversation of reason.”
It is her hope that her Vivid shows will be fit for purpose – to show people the reality of the reef and give them a space to both marvel and grieve
“But to grieve doesn’t mean that a thing is done – to grieve just means that you’re recognising where we are,” she says
“For an hour and a half you can come to the Great Barrier Reef with me
Without understanding what we’re looking at
there’s no hope of finding a direction forward
It’s actually a profound gesture of hope.”
Anohni and the Johnsons will perform Mourning the Great Barrier Reef at Sydney Opera House on 26 and 27 May as part of Vivid festival
The next phase of the transformative Ocean Reef Marina development is about to commence
with construction starting on the new headquarters for Marine Rescue Whitfords and facilities for the Ocean Reef Sea Sports Club and Joondalup City RSL
Western Australian developer Byte Construct has today been named as the preferred contractor for the works
which are set to get underway in the coming weeks
Marine Rescue Whitfords will be housed in a new two-storey building with space for training
The new facility will feature state-of-the-art amenities to support the crucial operations of Western Australia’s dedicated volunteer rescue service
representing a significant step forward in the Cook Government’s commitment to ensuring the safety and wellbeing of all who enjoy our coastal waters
three marine rescue vessels will be permanently moored at the marina on ready-access jetties for fast deployment
significantly improving safety for recreational boaters
fishers and other water users in Perth’s north
phone and online applications will allow every vessel to log trips from the coast to all local locations
improving safety and communications for all
The $6.48 million building has been specifically designed to accommodate Marine Rescue Whitfords along with the Department of Transport’s Marine Manager’s Office and services for future marina pen holders
It is an excellent example of cross-collaboration
with the Department of Transport and Marine Rescue Whitfords to work closely together to ensure the safety of the local recreational boating community
The neighbouring Ocean Reef Sea Sports Club and Joondalup City RSL will include upgraded angling
dive and sailing facilities as well as dining and bar options that will benefit current and future members
It will also offer improved meeting rooms for community groups and other local clubs to use
The City of Joondalup has put $3 million towards construction of the Ocean Reef Sea Sports Club
and the club itself has contributed $1.75 million
the redeveloped Ocean Reef Marina will be a premier waterfront precinct for Perth’s northern suburbs and a key tourism destination for WA
Premier Roger Cook said “The redeveloped Ocean Reef Marina will boast Perth’s first coastal pool
a family beach within the protection of the marina
upgraded facilities for local clubs and services
“Commencement of works on the new headquarters for Marine Rescue Whitfords and new Ocean Reef Sea Sports Club and Joondalup City RSL is a major milestone for the Ocean Reef Marina project
which has been made possible by my Government’s substantial $272.3 million investment
“We are investing in this generational development to provide another landmark tourism destination for WA
as we work to further diversify the State’s economy
“It will also deliver more housing options
improved services and unparalleled public amenities for the local community.”
Lands Minister John Carey said “The Marine Rescue Whitfords facility will feature state-of-the-art amenities
meticulously designed to support the crucial operations of our dedicated volunteer rescue service
“With dedicated pens ensuring a permanent rescue fleet
we are bolstering our ability to respond swiftly and effectively to emergencies along our coastline
“The new state-of-the-art clubhouse for the Ocean Reef Sea Sports Club and Joondalup City RSL will become an environmentally sustainable landmark within the newly developed Ocean Reef Marina
“It will offer upgraded dining and bar options
and sailing facilities and facilities for community groups.”
Emergency Services Minister Stephen Dawson said “Ensuring our emergency services volunteers have modern facilities and equipment to perform their life saving role is a priority for the Cook Government
three marine rescue vessels will be permanently located at the marina
ensuring faster deployment and enhanced safety outcomes for recreational boaters
“This is one of the biggest and busiest volunteer marine rescue groups in the State with around 250 call outs
“This new Marine Rescue Whitfords facility is a win-win for all concerned with the delivery of state-of-the-art amenities to support our volunteers and the local community.”
Joondalup MLA Emily Hamilton said “Our Joondalup community is excited to see the land-based works taking place and are looking forward to the new facilities that will provide a new home for Marine Rescue Whitfords
the Ocean Reef Sea Sport Club and the Joondalup City RSL
Joondalup is the city centre servicing our northern corridor and our new landmark Ocean Reef Marina will be a world-class tourism and hospitality destination that will boost our local economy.”
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Land and ocean temperatures reached new extremes in 2024
The annual average temperature across Australia in 2024 was the second highest on record after 2019
while the mean sea surface temperature around Australia was the highest on record.
This led to the fifth coral bleaching event in less than ten years in the Great Barrier Reef
as well as a severe bleaching event in Western Australia’s Ningaloo Reef.
invasive species and ongoing climate change continue to threaten our native ecosystems
41 species were added to Australia’s threatened species list in 2024
While a significant drop from the record 130 additions in 2023
it remains well above the long-term average of 25 species per year.
Australia’s environment scored a 7.7 out of 10 at the national scale
The three years prior saw the country score between 6.5 and 8.5 out of 10
after extremely low scores between 0.4 and 2.0 out of 10 in the disaster years of 2019 and 2020.
ANU Professor Albert Van Dijk warns the favourable environmental improvements of the last four years do not negate long-term concerns.
“Environmental conditions improved from 2023 to 2024 for most states and territories
Parts of South Australia experienced their driest year since at least 2000
leading to a state-wide score of 3.8 out of 10 in 2024 – the lowest in the country,” Professor Van Dijk said.
parts of inland Northern Territory experienced their wettest year in more than two decades
The territory recorded the best score in the country with 8.6 out of 10.
“New South Wales saw the biggest improvement from 2023
rainfall was well above average in January and March and again in November and December.
“Temperatures over Australia were the second highest on record with increased hot days
while snow cover fell to its lowest level since 2018
National rainfall was 18 per cent above the average
fire activity remained below average for the sixth consecutive year.
“Although environmental conditions were encouraging
this is largely the result of favourable short-term climate conditions rather than sustained long-term gains
the past year saw relatively good rainfall that allowed vegetation to thrive and soil health to improve
the global climate emergency continues to escalate
and Australia remains highly vulnerable.”
the report’s authors examine the Threatened Species Index
which looks at the trajectory of Australia’s threatened wildlife.
plants and frogs has declined by an average of 58 per cent,” report co-author Tayla Lawrie
from the Terrestrial Ecosystem Research Network (TERN)
Lawrie said the latest update offers a glimmer of hope
A slight two per cent increase for the most recent year of the Index (2021) suggests that declines may be stabilising for some groups
ongoing long-term monitoring is essential to confirm which species are improving and which continue to suffer.
Report co-author Shoshana Rapley from ANU points out that the devastating and long-lasting effects of the 2019/20 Black Summer bushfires on our nation’s biodiversity continues to reverberate.
the legacy of the Black Summer bushfires is still evident
with more than 50 per cent of species newly listed or uplisted on the threatened species list directly affected by the fires,” Rapley said.
14 species were uplisted to a higher category of extinction risk
Only one species was removed from the list – the southern bluefin tuna
It joins the short list of only 11 species that have successfully made it off the threatened species list due to population recovery."
2024 was Earth’s hottest year on record globally
while Australia’s per capita greenhouse gas emissions remain among the highest in the world
Professor Van Dijk said now is not the time for complacency.
businesses and individuals should act decisively to secure the future of Australia’s environment
Strategies such as investment in renewable energy
and increased biodiversity conservation efforts are essential to stop the underlying degrading trend,” he said.
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EPA is actively engaged in the U.S. Coral Reef Task Force (USCRTF)
The USCRTF was established by Executive Order 13089 to lead U.S
efforts to preserve and protect coral reef ecosystems
It is instrumental in building partnerships and strategies for on-the-ground action to conserve coral reefs
The USCRTF is co-chaired by the National Oceanic and Atmospheric Administration and the Department of the Interior with regular participation from 14 federal agencies
and commonwealths and three freely associated states
EPA participates on several USCRTF working groups
Recent products of these working groups that the EPA helped to develop include:
The Corals and Climate Adaptation Design Tool can be used by coral reef managers to incorporate climate-smart design into their programs and projects at any stage of planning and implementation
The tool has been used with partners in Guánica Bay
This Handbook on Coral Reef Impacts provides a review of the federal authorities
and territory roles and responsibilities; a compendium of current best practices—science-based methodologies for quantifying ecosystem functions or services; and a general overview of basic protocols available for use when assessing impacts to coral reef ecosystems and mitigating or restoring for unavoidable impacts to coral reef ecosystems
including the use of appropriate compensatory action to replace the lost functions and services
The USCRTF Watershed Partnership Initiative Priority Ecosystem Indicators document provides coastal managers
and watershed coordinators faced with modest budgets a suite of recommended ecological indicators and measurements to include in their watershed-specific monitoring plans
The recommended ecological indicators and measurements help determine the efficacy and evaluate the success of management efforts to reduce land-based sources of pollution on coral reef ecosystems
A user-friendly programmatic checklist developed to help managers and watershed coordinators identify programmatic needs for the successful implementation of a ridge to reef watershed management plan
and assessment; natural and social economic research and modeling; outreach and education; and management and stewardship
The U.S. Federal Government is a member of the International Coral Reef Initiative (ICRI),a partnership between Nations and organizations which strives to preserve coral reefs and related ecosystems around the world
Surveys from the air and on water show a few reef groups
such as the Ribbon Reefs in the far north and the Swains and Pompey reefs in the south
are consistently escaping severe bleaching while their neighbouring reefs suffer
But how? In our new research
we found their survival is due to cold water
most of these reefs are periodically bathed in cooler water even as other parts of the reef bake in marine heatwaves
This stems from the phenomenon called upwelling
where cooler waters from the deep mix with warm surface waters
These reefs are likely to be buffered from the worst of climate change
While the world’s oceans are heating up steadily
the deeper waters remain cooler than surface waters
Our modelling suggests cold currents could protect these vital refuges at least into the 2080s
even if continued high emissions lead to sea surface temperatures 2-3°C hotter than now
Safeguarding these refuges offers the best chance to preserve some of the reef’s rich array of species and – potentially – to allow corals to adapt to new heat regimes and eventually repopulate degraded reefs
heat stress can make coral polyps bleach by expelling their symbiotic algae
These colourful “zooxanthellae” algae provide coral energy and nutrition from photosynthesis in exchange for shelter
Bleached coral can recover if given a reprieve
Climate change is loading the dice for more heat, more often. This is why we are now seeing parts of the Great Barrier Reef record the worst coral loss in 39 years
we looked at why some reefs are less affected by heat
We found upwellings of cool water are protecting them
The reefs are climate refuges – areas where local conditions allow species to survive while other areas become unlivable
We define these cooler refuges as areas where average summer sea surface temperatures are at least 1°C cooler than nearby regions
These safer zones lie along the ends of the northern and southern Great Barrier Reef and run over 200 kilometres along the continental shelf
Off northern Australia in the eastern Torres Strait lie the Ribbon Reefs
These climate refuges are located near a steep continental slope with deep channels
a key refuge is the Swains and Pompeys reef complex
These reefs lie right on the continental drop off where the East Australian Current raises cold water closer to the surface
When strong tidal currents flood through narrow reef channels
cooler water from the deep can be drawn up over the continental shelf and mixed with warm surface water
acting like a cold bath for the fringing reefs and giving relief to coral
These effects can last up to a week or more
Currents can trap these cooler waters behind a long
we looked for unusually cool water in satellite temperature maps and ocean models
to see if these life-sustaining cool flows would persist in the 2050s under a high emissions scenario
The good news: currents of cool water will continue at least to 2080
This is because even as surface waters warm and marine heatwaves arrive more often
the currents carrying cooler water to the surface in these refuge reefs will continue
even deeper waters will warm to a level that coral cannot tolerate
the South Equatorial Current carries warm water westward toward the Barrier Reef but then splits into the north-flowing Gulf of Papua Current and the south-flowing East Australian Current
Our research found the location of the split is steadily moving southward
This could change where current-dependent larvae of coral and coral-eating crown of thorns starfish end up
But our modelling shows these changes won’t greatly affect upwellings over our time period
damage from shipping and crown of thorns outbreaks also pose threats to these remote reefs
That’s not to say we should give up on tackling threats to the reef more broadly – only that these reefs are particularly valuable
Could coral on these more protected reefs adapt fast enough to take advantage of cool upwellings
could heat-adapted coral larvae repopulate worse-hit areas
some version of the Great Barrier Reef might survive
Sharply reducing emissions is our best option to control global warming and help the Great Barrier Reef endure into the next century
This article is republished from The Conversation under a Creative Commons license. Read the original article
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Latest Earthquakes
Calif. — A new study shows coral reef restoration in Florida and Puerto Rico could save thousands of lives and prevent hundreds of millions of dollars in damage and economic disruption each year
Restoration efforts would most benefit children
Researchers developed a modeling system to quantify the value coral reef restoration could provide to 1,000 kilometers
The research compared how much flooding storms could cause with and without coral reef restoration at a 10 square meter
Researchers then determined how many people and how much property and economic activity reef restoration could protect by preventing coastal flooding
"Coral reefs are natural coastal barriers that can substantially reduce coastal flooding and erosion,” said Curt Storlazzi
lead author and research geologist from the U.S
we've lost a lot of reefs to global and local stressors and restoring them can re-establish the protection they once provided."
Reefs can absorb and weaken damaging waves
waves that hit shores are smaller and cause less flooding and erosion
Restoring degraded or destroyed coral reefs could protect nearly 3,000 people each year in Florida and Puerto Rico alone
Reefs could also prevent more than $391 million in damage to property and lost economic activity annually
Using a budget of $3 million per kilometer
the study calculates a benefit-to-cost analysis of reef restoration and maintenance
About half of the budget is allocated to establishing reefs and the other half to maintenance
the value of property and economic activity protected from storm damage would be greater than the cost of reef restoration
“This approach represents a massive advance in characterizing the effectiveness of nature-based infrastructure for coastal protection
Modeling benefit-to-cost of protection and/or restoration can also be applied to other ecosystems
this modeling system can be used to assess the impacts of future changes in storms or sea level
helping us to measure when and how cost effective it is to adapt.”
Vulnerable populations are disproportionately exposed to risks from natural hazards
Restoration could provide monumental benefits to the people who most need help
This study shows that vulnerable populations could receive two- to three times more protection from flooding relative to the general population
“Our goal in this study was to provide sound science to identify who benefits from restoration and where those benefits are felt most,” said Storlazzi
"We want people to understand that restoring coral reefs isn't just about protecting beautiful and diverse habitats
This study also provides a framework to calculate benefit-to-cost analyses for coral reef restoration in hazard risk reduction
This establishes an avenue for coral restoration projects to be considered for post-disaster mitigation funding from agencies like the Federal Emergency Management Agency or the U.S
alongside traditional risk-reduction methods such as bulkheads or breakwaters
Coral reef restoration can be longer lasting than manmade structures alone
manmade structures like levees or seawalls would need to be made taller
coral reefs are living animals and can grow with changing sea levels
“Most hazard mitigation and disaster recovery funding supports artificial infrastructure
Director of the UCSC Center for Coastal Climate Resilience and a co-lead on the project
“By valuing the benefits of natural infrastructure
we level the playing field and open major new funding opportunities for reef restoration.”
What about the value coral reefs provide industries such as tourism
This study only considers the economic benefits of avoided damage
the true economic value of coral reef restoration is likely much higher
The new study by the U.S. Geological Survey, University of California, Santa Cruz, and the National Oceanic and Atmospheric Administration titled “Hybrid coral reef restoration can be a cost-effective nature-based solution to provide protection to vulnerable coastal populations” was published today in the journal Science Advances. DOI: 10.1126/sciadv.adn4004
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Climate change poses a major threat to coral reefs. Download this infographic | Infographic Text
Climate change is the greatest global threat to coral reef ecosystems
Scientific evidence now clearly indicates that the Earth's atmosphere and ocean are warming
and that these changes are primarily due to greenhouse gases derived from human activities
Climate change will affect coral reef ecosystems
changes to the frequency and intensity of tropical storms
all of these impacts dramatically alter ecosystem function
as well as the goods and services coral reef ecosystems provide to people around the globe
Increased greenhouse gases from human activities result in climate change and ocean acidification
The world's ocean is a massive sink that absorbs carbon dioxide (CO2)
Contributing factors that increase greenhouse gases in the atmosphere include burning fossil fuels for heat and energy
Shrink your carbon footprint to reduce greenhouse gases
Do your part to help improve overall coral reef condition
Many coastal and island communities depend on coral reef fisheries
but overfishing can deplete key reef species and damage coral habitat
When the water off the coast of Florida reached nearly 38C last year
turning deathly white after corals ejected the symbiotic algae that provide them with food via photosynthesis
The Coral Restoration Foundation (CRF), based in the Florida Keys, cultivates coral in 6,000 square metres of ocean-based nurseries. It lost half of the corals it was rearing in nurseries for transplantation onto the region’s degraded reefs, and suffered the near-total death of the threatened acroporid corals it had been painstakingly restoring
It was a major blow to efforts to restore damaged reefs
and symptomatic of how the current playbook for helping corals in uncomfortably hot water is struggling to cope with surging temperatures
The state of coral reefs globally has led to increasingly alarming warnings from scientists, as ocean temperatures have broken records month after month in 2023 and 2024. After summer 2023, the US National Oceanic and Atmospheric Administration (NOAA) extended its alert scale for coral heat warnings
the highest being “near complete mortality”
“Each time we break and blast through records
even for the scientific community,” says Lizzie McLeod
global ocean director at The Nature Conservancy
Attempts to restore depleted coral cover through coral gardening
assisted migration (by harvesting larvae) and assisted evolution (rearing corals in an aquarium) are prohibitively expensive and unworkable at any meaningful scale
Coral reefs cover less than 1 per cent of the world’s surface area, yet support 25 per cent of all marine species. Vital for coastal communities, an estimated one billion people rely on them for food and livelihoods
A vast number of homes and businesses are protected from damage during storms by reefs that dissipate the power of waves
As concern has grown, attempts to protect reefs from heat have spread. Protective screens have been erected as underwater parasols over some reefs. Divers have been banned from popular areas to reduce potential damage. In some cases, corals have been physically moved to deeper
cooler waters or taken out of the ocean entirely for safekeeping in aquariums
There has also been a surge of interest in reef restoration projects, which have proliferated around the world. Many focus on identifying those species and locations where corals are proving more resilient to heat stress
Their genetics are then reproduced using cultivated coral to restore damaged reefs and make them more resilient to climate change
transplanting and re-attaching coral colonies or branch fragments to repair a degraded site – is expensive and labour-intensive
because it requires very large numbers of corals per hectare
Some scientists are sceptical that such projects are viable for the long-term survival of reefs
a consortium of G20 countries and the International Coral Reef Initiative said new restoration tools were needed
because most methods were suitable only for small-scale intervention
In March, professor Terry Hughes of Australia’s James Cook University wrote: “Attempts to restore depleted coral cover through coral gardening
assisted migration (by harvesting larvae) and assisted evolution (rearing corals in an aquarium) are prohibitively expensive and unworkable at any meaningful scale.”
Hughes was citing a recent feasibility study conducted by the Australian government that eliminated the option of assisted migration, due to its risks. Another study
found the Great Barrier Reef would need an additional 10,000 hectares of coral tissue to increase its coral cover by just 1 per cent
The Florida team remains upbeat after their 2023 setback
and evacuated representative samples of corals to onshore facilities to try and safeguard the reef’s genetic diversity
Lessons learned from other extreme weather events also helped
When hurricane Irma hit the Florida Keys in 2017
it wiped out around 50 per cent of all the corals the team had restored since it started work in 2007
CRF’s senior director of strategic engagement
she says her teams restored more coral than in the 10 years leading up to it
The reefs off Florida are among the most degraded in the world due to pollution, climate change and other pressures. They were at just 2 per cent of their historical range before the most recent bleaching
But Grainger remains positive her programme can help turn things around
“We’re very confident that in the next two to three years we’ll be able to get as many corals back onto the [restored] reefs as we lost last year,” she says
The experience will help the group improve the resilience of its nurseries and its future programmes
Last year’s heat also shed new light on the genetic diversity of coral
Grainger says the same species of coral reacted differently depending on location
demonstrating that coral resilience hinges on multiple factors including bacteria and viruses around the coral
“Corals that were very resilient in one location were not the same in another
That’s really critical – there is resilience in genetic diversity,” she says
Others see hope in improved collaboration to accelerate the sharing of discoveries on how corals respond to heat
the insights into coral genetics that were made possible by Grainger’s team of scientists
With this acceleration in mind, the Marine Ecological Research Management AID (Mermaid) open-source platform was created in 2020 by the Wildlife Conservation Society (WCS)
Researchers collect reef data underwater with pencils and clipboards
This has traditionally been followed by hours of manual data entry and checking using spreadsheets
director of coral reef conservation at the WCS
such laborious data-logging processes have significantly delayed decisions on how to manage reefs
more than 2,000 scientists in 35 countries can now put their clipboard observations on reef health directly into the platform
This makes them available to colleagues much more quickly
where community elders decided to close their local marine reserve to fishing after scientists using Mermaid were able to share data directly with them
The data showed that though the reef was recovering from a cyclone in 2016
fish populations were still below sustainable thresholds
“Tools like Mermaid can really bring together this data at the scales and on the timelines that are needed,” she says
“It’s just unacceptable that we don’t have a global picture of the status and trends of coral reefs that’s not already years out of date.”
The Nature Conservancy is also stepping up collaboration. Its “super reefs” project aims to identify areas of coral that do less badly in warmer water and therefore have potential to reseed neighbouring reefs
It wants the findings to be quickly translated into lessons for restoration practitioners and applied in the field
“There’s often a miscommunication between scientists and conservationists
A lot of great research is never applied,” says Annick Cros
there are requests from reef managers that are not heard by researchers.”
Run in collaboration with the Woods Hole Oceanographic Institution and Stanford University in the US
the project is currently searching for super reefs in the Marshall Islands and the Bahamas
Scientists working for the UN’s climate science body, the Intergovernmental Panel on Climate Change, predict that reefs will decline by a further 70-90 per cent at 1.5°C of global warming above pre-industrial temperatures
with losses of more than 99 per cent at 2°C
Understanding and restoring reefs is therefore just one part of the equation needed to save coral in the long-term; drastic reductions in greenhouse gases and local pollution are also vital
“Our role is not necessarily to maintain reefs the way we know them today,” Cros says
“It is to keep the ecosystem functioning for as long as we can to give communities time to either change livelihood
and for us to come up with better solutions for climate change and all the other things that are impacting reefs.”
Grainger says banking the genetic material of the corals is effectively “putting our finger in the dam”
“We’re working to restore these ecosystems for the communities that depend on them – we can’t abandon them
even if our work is wiped out every 10 years,” she says
“We’re keeping these [coral] populations from going extinct
and we have the capacity to bring them back on a massive scale
But if we don’t work towards a carbon-negative future
then coral reefs really don’t stand a chance.”
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Metrics details
We identified four primary substrate types: coral
with algae-covered substrate predominating and projected to persist
Our results underscore the urgency of monitoring reef health and highlight the potential limitations of satellite assessment
This research enhances understanding of reef dynamics and offers a framework for identifying vulnerable areas
which are crucial for effective conservation efforts
New web-mapping software allows cross-referencing findings with aerial imagery to indicate impact on calculated area or quantify reef substrate type
further investigation into the current reef structures of Barbados is both timely and critical
leveraging advanced technology to reassess and enhance conservation strategies
As the MPA covers the middle region and has high protection levels
we propose the middle region will have low area loss and a low rate of change
previously categorized as highly degraded in 1996 with low protection levels
will have a higher rate of change and overall higher area loss
Rate of change in surface area of reef sites from 1950–1991 (left) and 1991–2023 (right)
Decadal changes in surface area of reefs based on location from (2013–2023)
Clustering of decadal percent loss changes in reefs based on location
The value in the parenthesis represents the standard deviation of the average percent loss
with the highest loss being Six Mens with 24% loss
followed by Heywoods (23.24%) and Paynes Bay 1 (23.42%) in 1991
Identified substrate and predicted dispersal of substrate across Bellairs (A), Sandy Lane (B), and Paynes Bay (C) (Satellite imagery and maps were created using ArcGIS Pro (version 3.2.2). Available at: https://www.esri.com/en-us/arcgis/products/arcgis-pro/overview.)
where a combination of fisherman extraction and tourism indicated a continuous decrease in the spatial change of coral colonies from 1980 to 2018
Heywood (A and B) and Paradise Beach (C and D) from 2013 (left column) and 2022 (right column) with and without anthropogenic developmental (artificial breakers and dredging ) impacts (Satellite imagery and maps in this figure was generated using Google Earth Pro (version 7.3.6.9796). Available at: https://www.google.com/earth/versions/#earth-pro)
This underscores the critical importance of ground-truthing and considering the nearest-neighbor relation
which better entails analyzing the spatial relationships between reef sites to understand substrate variations and ecological dynamics
the same processes and pattern observations need to be recognized widely and consistently applied to coral ecosystem work
This could combat further shifts and hopefully sustain the overall available area and present substrate
integrating various research findings and methodologies provides valuable insights into the complex dynamics of coral reef ecosystems
It underscores the urgency of implementing holistic management strategies to safeguard these invaluable marine habitats
Our reef structures are degrading in some areas but can be effectively monitored with satellite for structure assessments if ground-truthing for substrate conditions is conducted
many organizations have maximized their reach into the oceans and created higher-resolution open-access ocean assessment tools
With the continuation of developments like this
assessments that could tackle structure and substrate are soon to come
Further exploration into the temporal dynamics of substrate alterations and their consequential impact on overall reef area loss would provide critical knowledge
Reef Site Locations along the West Coast of Barbados (Satellite imagery and maps were created using ArcGIS Pro (version 3.2.2). Available at: https://www.esri.com/en-us/arcgis/products/arcgis-pro/overview.)
Flow chart of reef site assessment methods for both polygon processing and substrate verification
The total number of included reefs analyzed for the rate of change in reef surface area was 18
Fourteen of Lewis’ original 20 were included in this analysis
Each reef was measured in ArcGIS Pro Version 3.2 using polygons for perimeter and surface area
The equation Rate = \(\:{(x}_{1\:\:}-\:{{x}_{2})/({y}_{1\:}\:-\:{y}_{2})}_{}\)was used where the numerator represents the surface area at a specific year (\(\:{(x}_{1\:\:}\)and \(\:{(x}_{2\:\:}\))
and the denominator (\(\:{y}_{1\:}\)and \(\:{y}_{2}\))represents the change with respect to time (or the difference between the observation years)
This equation allows us to measure how quickly the surface area changes over time
The size of the rate of change in surface area tells us how fast the change is happening
we decided to consider location again and include a protection level
All reefs were kept for further decadal analysis
with the addition of DeadTree reef due to its proximity to the other reefs
A random intercept mixed effect linear regression model estimated via maximum likelihood with year as a level-1 variable was fitted to identify any significant change to Surface Area and Year
To assess decadal change comparing 2013 to 2023
paired t-tests and a random intercept linear mixed effect model estimated via maximum likelihood with year as a level-1 variable and protection level and location as level-2 variables were conducted
Assumptions for the normality of residuals were examined post hoc and adequately met
Mixed effects models were performed using the R packages nlme Version 4_1.1–35.1
The final best-fitting mixed effect model based on BIC was estimated using an AR(1) covariance matrix
Cluster analysis was performed utilizing Gower Distance
This approach supports both quantitative and qualitative variables
Reefs that were not missing surface area in 2013 and 2023 were included in the analysis
The optimal number of clusters (k = 4) was determined using silhouette plots
The cluster plot was constructed using the k-medoids algorithm
Features considered for clustering included location
Cluster analysis was performed using the R packages cluster Version 2.1.6 and factoextra Version 1.0.7
Average cluster values were calculated because they play a crucial role in cluster analysis as they provide insight into the distribution and composition of clusters
Calculated estimations were rendered to depict surface area in 1950
and 2023 based on available data and drawings
These serve as visualizations of predicted reef layouts at previously highly degraded locations
2023 GPS coordinates as geotagged images taken while ground truthing for both Sandy Lane locations (Satellite imagery and maps were created using ArcGIS Pro (version 3.2.2). Available at: https://www.esri.com/en-us/arcgis/products/arcgis-pro/overview.)
This was derived to identify ecological shifts in the environment
the development of rubble as a potential habitat
and to understand what parts of the originally identified reef were categorized as hard coral
Coral is defined as hard coral or hard standardized substrate that is not white (bleached) or deep brown (dead)
Algae was defined as smothering organisms on hard surfaces
Rubble was described as a hard substrate completely covered in sediment with randomized texture and/or pattern
sand was defined as no hard substrate present and only uniform soft terrain where any attachment is rare (see examples of substrate categories in Supplementary Figure S7)
Substrate identification visual verification method: coral identified geotag image example and classification descriptions of each section
ArcGIS Pro Version 3.2 was used for substrate layer descriptive analysis and processing
To identify the reliability or agreement of our substrate results from each verification method
an Intraclass Correlation Coefficient or ICC was conducted
All analyzed images were converted to substrate-categorized GPS points and deposited onto five of their corresponding reef sites
Geotagged images were sorted by site and substrate category using color
Each geotagged point was used to predict the regional substrate for the edge of each reef site
A 25-meter buffer was applied to limit analytics to the designated research site
Calculated estimations were then rendered to depict visualizations of predicted and identified substrates at each location (see Supplementary Information for details on interpolated map layering)
Raw satellite imagery for Barbados from 2013 to 2023 is available on Google Earth Pro
and code required to generate percent loss
and further analysis are available upon request
Please use email listed for the corresponding author
Community involvement in management for maintaining coral reef resilience and biodiversity in southern Caribbean marine protected areas
Economic Implications of Coral reef Degradation
Ecosystem management tools to study natural habitats as wave damping structures and coastal protection mechanisms
Coral reefs are critical for our food supply
One-third of reef-building corals face elevated extinction risk from climate change and local impacts
Towards modelling the future risk of cyclone wave damage to the world’s coral reefs
Stony coral tissue loss disease decimated Caribbean coral populations and reshaped reef functionality
Tosic, M. Impacts of landuse and runoff water quality on coral reef environments in Barbados. (2007). https://escholarship.mcgill.ca/concern/theses/5t34sn113
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Apparent timing of density banding in the Caribbean coral Siderastrea siderea suggests complex role of key physiological variables
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Caribbean Natural Resources Institute (CANARI) Technical Report 281
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The impact of tourism and personal leisure transport on coastal environments: A review
Detection of coral reefs degradation using geospatial techniques around Saint Martin’s Island
A metagenomic-based study of two sites from the Barbadian reef system
Limitations to coral recovery along an environmental stress gradient
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Material legacies can degrade resilience: Structure-retaining disturbances promote regime shifts on coral reefs
Coral rubble dynamics in the Anthropocene and implications for reef recovery
Evaluating the precariousness of coral recovery when coral and macroalgae are alternative basins of attraction
Terrestrial degradation impacts on coral reef health: Evidence from the Caribbean
Land use impacts on coral reef health: A Ridge-to-reef perspective
Translating the 10 golden rules of reforestation for coral reef restoration
A benthic substrate classification method for seabed images using deep learning: Application to management of deep-sea coral reefs
Using coral color to indicate coral health in five caribbean species
Coral point count with excel extensions (CPCe): A visual Basic program for the determination of coral and substrate coverage using random point count methodology
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In IOP Conference Series: Earth and Environmental Science
A quick and clean photographic method for the description of coral reef habitats
Download references
This research was funded by a Level 1 grant from the National Geographic Society and by the International Coral Reef Society Ruth Gates Award
All permits were acquired from the Coastal Zone Management Unit (CZMU) for coral reef research (REF CZO1/9/94-183)
We thank the NSF Advanced Studies Institutes (ASI) program (NSF OISE-2154238) in Advanced Studies of Coastal Marine Environments
for inspiring our research through their instruction of advanced computing techniques
which prompted our exploration into the concept discussed in this publication
We thank Ashlyn Ford for assisting with all fieldwork and outdoor data collection and Micah Floyd for visualization assistance
the University of the West Indies Cave Hill
and the McGill Research Station for their immense support
and assistance in bringing this project to fruition
Marine and Environmental Science Department
University of North Carolina at Chapel Hill
performed project administration responsibilities
and conducted fieldwork with a volunteer diver
AG carried out substrate analysis and created the resulting figures
and SL performed mixed effect and cluster analyses and rendered the resulting figures
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations
Below is the link to the electronic supplementary material
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DOI: https://doi.org/10.1038/s41598-024-83720-w
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While April - and Earth Month - may now have passed, here at MC UK, we celebrate protecting our planet, eco-preservation, and doing your bit for the earth year-round. That said, the month does offer us a moment to reflect on the current state of the climate. While most of us are doing our bit to embrace sustainable living
That said, in an era of climate anxiety and concern over greenwashing and the declining rainforest, it’s not always easy to find stories that feel hopeful. While we can do our best to shop B-Corp brands
sustainable fashion brands and do our small part for the planet
But deep under the sea is one place where hope is desperately needed - and can be found
and if you’re looking for something hopeful to inspire your actions
“Your lives are dependent on reefs in some way or another, even if you never see one,” says Professor David Smith, Chief Marine Scientist at Mars
a fisherman shares how his neighbours’ homes have been washed away by coastal erosion
But Reef Builders offers something rare in environmental storytelling: hope
A post shared by The Sheba Hope Grows™ Program (@shebahopegrows)
That’s the question at the heart of Reef Builders, a new documentary presented by Sheba
which follows one of the world’s largest and most ambitious coral restoration programmes
The film offers a rare look at how restoration works and how different communities are coming together to make it happen
The initiative takes place in more than 70 active sites across Indonesia
and Hawai’i and shows that coral restoration isn’t just possible
but extremely powerful when we come together to take action
At its core is the ‘Reef Star’: a handmade
star-shaped steel structure placed on degraded reefs
giving coral fragments a stable surface to grow on
“The art of restoration is really about giving nature a little energy,” explains Professor Smith
“You’re not rebuilding from scratch… you’re just helping the reef remember how to heal itself.”
What makes Reef Builders stand out from other climate documentaries
is its focus on the people behind the science
and associate producer on the project - puts it: “I wanted to give our flowers to the people already doing the work
the local communities who come together to rebuild the reef
The film captures what restoration really looks like: collaboration
“I was surprised by how fast coral can grow when given the chance,” Cravalho tells Marie Claire UK
“It’s a man-made solution to a man-made problem
At a time when climate storytelling can feel rather heavy or even hopeless
Reef Builders offers something rare: a story of recovery
they have day jobs,” Cravalho tells Marie Claire UK
“And they still give their time to restore the ocean
“I don’t have a scientific degree,” she said
“But I think I make up for that with excitement… I love being young
and getting to show that we can all be part of this
“Our creation story begins with the coral polyp,” she added
and not separated by it - by a species of coral that can’t even speak - that’s what brought us together.”
As Professor David Smith puts it: “We are an island nation
and the ocean needs coral reefs to function properly.”
“We don’t need a thousand scientists,” Smith says
Metrics details
Autonomous Reef Monitoring Structures (ARMS) are used worldwide to assess cryptic diversity
such as immersion duration and/or deployment and retrieval seasons
Here we studied temporal and seasonal variability in coral reef cryptic communities sampled with 15 ARMS on a single coral reef slope site at Reunion Island
Settlement patterns and temporal succession of Eukaryote communities were investigated across three immersion times (6 months
Both markers detected different taxa with different resolutions
but broadly similar patterns of community composition and structure
While OTU diversity of communities did not change with immersion time and season
these parameters significantly affected community structure and composition
Our results showed a decrease of the similarity of ARMS communities with duration of immersion
and a strong temporal turnover of species with only a small proportion of the diversity persisting over time
The small proportion of OTUs assigned at phylum level highlights the uniqueness of the Mascarene cryptobiome
We further presumed that community composition will change over time
with short immersion times (6 months) reflecting the early colonizers community and the two longer immersion times reflecting later successional stages
If the ecological succession is driven by deterministic processes
we expect to observe an increasing similarity among ARMS replicates over time
if the succession is driven by stochastic events
the similarity among ARMS replicates is expected to decrease
reflecting the different succession trajectories of the cryptic reef communities in ARMS replicates
numerous reef species have reproductive seasonality
when light and temperature reach their annual maxima
we expect to observe differences in community composition according to the season of deployment or retrieval
(a) Schematic view of an Autonomous Reef Monitoring Structure (ARMS); (b) Timeline of deployment and retrieval of the 5 batches of triplicate ARMS used in this study
The red/blue colour gradient on the bars represents the seasonality and thus the seawater temperature: red for hot season
blue for cool season and purple for both inter-seasons
taxonomy was assigned against both local and SILVA 138.1 databases using hierarchical steps: 1/ blast against local database of 164 unique sequences at 99% similarity (qiime feature-classifier classify-consensus-blast); 2/ identification of the Last Common Ancestor (LCA) with a threshold of 99% similarity against MIDORI; 3/ LCA method with a threshold of 97% similarity against the local and SILVA 138.1 databases merged
Seasonal variations in environmental parameters were tested using one-way ANOVA and when significant effects were detected
post-hoc Tukey tests with single-step adjustment of probability were conducted
Environmental parameters during the study period
Dashed lines represent the smoothed means under a GAM model
After processing and filtering, the 18S dataset contained a total of 5,621 OTUs, of which 959 OTUs (17%) were assigned to Eukaryota (Table 1)
The COI datasets contained a total of 4,722 (OTU99) and 4,870 (OTU97) OTUs
but only 438 (OTU99; 9.3%) and 316 (OTU97; 6.4%) were assigned to Eukaryota
and only half of these could be assigned to species level
Composition of the assemblages at taxa category level for each molecular marker (horizontal blocks) and each fraction (vertical blocks)
Letter codes below plots indicate the season of deployment and retrieval: C = cool
the immersion time of ARMS significantly affected the cryptobiome communities retrieved
they were significantly different among the three immersion times at the ARMS level (pairwise.adonis
the communities retrieved after 1 year differed significantly from those retrieved after shorter or longer times (pairwise.adonis
the community after 6 months was significantly different from the one after 1 year immersion (pairwise.adonis
the communities present at the ARMS level after 6 month immersion differed significantly from the one after immersion for 1 year (pairwise.adonis
the communities recovered after 1 year were significantly different from those recovered after shorter or longer immersion times (pairwise.adonis
the communities were significantly different between all three immersion times (pairwise.adonis
The linear mixed-effect models including random effect of ARMS were not significantly different from the more parsimonious models with only the fixed effect of the immersion time
Between ARMS batches immersed for 1 year and for 2 years
the Simper analyses highlighted a decrease of solitary ascidians (Class Stolidobranchia) and an increase in colonial ascidians (Class Aplousobranchia) in the 106–500 µm and sessile fractions of the 18S marker
The 18S marker also showed a general trend of higher abundance (reads numbers) of Rhodophyta (but not Ceramiales) in the hot season
Number and proportion of unique and shared OTU99% for the COI among the three immersion times for the datasets ARMS level and the three fractions. Ellipse sizes are proportional.
Ternary plots of Jaccard similarity and the partitions of beta diversity (replacement and richness difference) at ARMS level and for the three fractions obtained from the OTU99% of the COI metabarcoding
Ternary plots are shown for the total experiment (All) as well as within modalities and within and among immersion times
Red dots and numbers in brackets on the axis labels represent the mean values of each diversity component
Increasing immersion times resulted in decreasing community similarity among ARMS replicates (ESM 17)
for the ARMS deployed during the hot season for which three immersion times were available
the similarities among 6-months replicates reached 38 ± 3% whereas the similarities among 2-years ARMS were 29 ± 3%
While there was no significant difference between the intra-modality similarities of the three immersion times (KW
the similarities among intra-modalities were significantly higher than similarity among two modalities (6 months vs
The analyses of the beta diversity component showed an increased species replacement between 6 months (48 ± 10%) and 1 year (57 ± 2%) followed by increasing richness differences among replicates between 1 (10 ± 4%) and 2 years (19 ± 12%) of immersion (ESM 17.2) although those differences were not significant (KW
however these differences in Jaccard similarities were not significant; KW
Comparison of our results with previous studies also needs to consider (1) the OTU clustering threshold; (2) the filtration step (removing bacteria or keeping only a subset of taxa
like metazoans); (3) the completeness of the local reference database and (4) the number of sites studied
thus diminishing the numbers of assigned COI OTUs
The DNA of mobile organisms found in the sessile fraction might be cellular debris especially for fish
while gastropod eggs and symbiotic shrimps living inside sponges or ascidians were also observed
the DNA of the sessile organisms found in the filtered samples may come from propagules and larvae or more likely due to some debris of organisms present on the plates
which were disassembled in the same ARMS water
we observed a decrease of annelid diversity with immersion time
while arthropods reached their maximum diversity in 1-year ARMS (especially those deployed and retrieved in the hot season)
showed that the top-down control by fish feeding plays a more important role during early succession (< 1 year) while environmental factors may become more important during later successional stages
ARMS communities with immersion times longer than two years may tend to be more similar
Further studies with longer immersion times will be necessary to reach community maturity (climax stage) and understand the processes leading to it
The study site on Reunion’s outer reef slope was subject to seasonal variations in environmental conditions
The spatio-temporal dynamics of cryptic communities may therefore be linked to this seasonal variability
this study is the first to highlight the role of season in shaping the composition of communities sampled by ARMS
alpha diversity was not significantly different between hot and cool seasons and the richness difference values remained low
the seasonal variations in coral reef communities include complex interactions of environmental factors
Taxon-specific studies are needed to better understand the implications of such seasonal variations with the need for building a local reference database for molecular identification of taxa
This study showed that both immersion duration and season affect the composition of the communities sampled by ARMS
Both parameters need to be taken into account in designing a sampling plan and in data analysis
We therefore recommend to deploy and retrieve ARMS during the same time of year or season
As the number of OTUs do not increase with immersion duration
a year-by-year basis of ARMS deployment and recovery may allow for a more rapid assessment of changes in cryptobiome communities than the conventional immersion duration of 2 years
Short immersion times are often more compatible with project funding timeframes and also reduce the risk of losing ARMS units (e.g.
Given the lack of available base-line data on the temporal dynamics of the cryptobiome
carrying out a short pilot study aiming to evaluate possible seasonal effects
before starting a longer-term monitoring program
would likely further improve the interpretation of the results
the effects of immersion time and season on cryptic communities collected by ARMS were analysed systematically for the first time here
Our results show that both factors need to be considered in monitoring or quantifying cryptobiome diversity patterns using ARMS
and probably other standardized approaches
While the overall number of OTUs collected with ARMS does not seem to depend on the immersion time or the deployment and/or retrieval season
Analyses of beta diversity suggest an initial colonisation of ARMS plates by pool of pioneer taxa
these are partly replaced due to the stochastic arrival of later successional taxa which
lead to different communities in ARMS replicates
only a small proportion of the cryptobiome community remains stable over time
the season during which ARMS were deployed seems to have a greater effect on the taxa recovered than the retrieval season itself
Sessile organisms appear to be more sensitive to seasonal effects
Although we deployed 15 ARMS in the same location (a single site at a single depth on an outer reef slope in Reunion)
this sampling effort was not sufficient to recover the total cryptobiome diversity of that site
underscoring the overwhelming diversity of cryptic species present in the reef frame
the small fraction of diversity that can presently be assigned highlights the uniqueness of the Mascarene cryptobiome and the need for further sampling
identification and sequencing of these communities
Raw reads produced in this study were deposited under the GenBank BioProject: PRJNA1061095 (https://www.ncbi.nlm.nih.gov/bioproject/PRJNA1061095). R code and databases to reproduce findings are available on MC Github repository (http://github.com/Mcouedel/ARMS_metabarcoding_temporal)
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Sources of particulate organic matter at the ecosystem scale: A stable isotope and trace element study in a tropical coral reef
Sediment characteristics in reef areas influenced by eutrophication-related alterations of benthic communities and bioerosion processes
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This study was supported by the research program Fonds européen de développement régional (FEDER) 20171591-0002633 CALIBIOME 2017-2022
ARMS deployments at Reunion were conducted under permit n°2020-09-DEAL/SEB/UBIO of the Direction de l’environnement
de l’aménagement et du logement de La Réunion
and permit n°2020-054 of the Direction de la mer Sud océan Indien
Sampling was in conformity to the Nagoya protocol (declaration n°3040030)
The participation to the processing of ARMS samples of Sophie Bureau
the Master students Gwennaïs Fustemberg and Auriane Serval
and the BSc student Amélie Verde Ferreira is greatly appreciated
Marion Couëdel was supported by a PhD fellowship provided by the European Union FSE programme
The authors thank all the persons who helped during field sampling and lab work
Laboratory work was made possible by the Service de Systématique Moléculaire of the MNHN (UAR 2700 2AD)
We are grateful to Emmanuel Corse and Matthieu Leray for their advice on lab work and bioinformatics process
and Eric Goberville for his comments on the revised manuscript
we thank the reviewers for constructive comments on an earlier version of the manuscript
UMR 9220 ENTROPIE (Université de La Réunion
Muséum national d’Histoire naturelle (MNHN)
AD and MC conceptualized the project and HB
MG and AD acquired the funding for the project
wrote the main manuscript text and prepared the figures
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DOI: https://doi.org/10.1038/s41598-024-76834-8
Conservationists fear fallout from president’s proclamation on fishing in federally protected area of Pacific Ocean
a federally protected area in the central Pacific Ocean spanning nearly 500,000 sq miles
As one of the most pristine tropical marine environments in the world
the monument is now at risk following Trump’s decision last week to unleash American commercial fishing in the area with far-reaching environmental consequences
Read moreIn addition to being home to many threatened
endangered and depleted species including 22 kinds of seabirds
the monument contains fragile ecosystems surrounding some of the world’s most ancient coral colonies
to “amend or repeal all burdensome regulations that restrict commercial fishing” in the area
As part of his quest to make the US the “world’s dominant seafood leader”, Trump called the regulations “so horrible and so stupid”
saying that American fishers are being “forced to go and travel four to seven days to go and fish in an area that’s not as good”
View image in fullscreenA map showing Pacific Marine national monuments
an attorney for the environmental conservation group Earthjustice
pushed back on Trump’s claims that federal regulations are hindering American fishers
“When he is saying that fisher folks from Hawaii or American Samoa need to travel for days to go fish. Well, you need to travel for days to get to these remote Pacific islands
They’re some of the most remote places on Earth … and they’re certainly not right next to Hawaii,” Henkin said
According to a 2023 study, in the last five years, the US-flagged purse-seine fleet only spent 0.52% of their effort fishing in the two areas where commercial fishing is currently allowed in the Pacific Islands Heritage area.
Echoing similar sentiments as Henkin, David McGuire, the founder of the shark conservation group Shark Stewards, said: “It’s grandstanding … These fishermen don’t travel 2,000 or 3,000 miles … They’re already out there, four or five hundred miles. There is no incentive for them to go to the more central islands.”
you won’t have the science and you won’t have the management biologists in Washington or elsewhere at universities that are funded by National Fisheries or Noaa,” McGuire said
Other concerns surrounding the proclamation’s environmental impact is the potential rise in illegal fishing as well as bycatch. Research has shown that illegal
unreported and unregulated fishing (IUU) accounts for one of every five fish caught in the wild
Greenpeace’s US project lead on ocean sanctuaries
said: “Having a legal commercial fishery provides cover for illegal fishing
If you just see a fishing boat going through waters
you are not there watching what they’re catching.”
Furthermore, despite sharks playing a critical role in maintaining healthy ecosystems, more than 100m of the oft-misunderstood animals are killed every year as part of bycatch and shark-finning
It’s a special piece of America… It’s as if we had just allowed commercial hunting into a place like YellowstoneDouglas McCauley
a marine biology professor at the University of California
warned that the proclamation can have profound impacts on shark conservation
“You can catch a lot of the tuna that you want
but you also catch and kill many sharks,” he said
Yet Trump’s proclamation can rapidly undo years of shark conservation in just minutes
“If you open up a section of ocean that has all of these very long-lived
you can decimate 100 years of conservation in almost 15 minutes of fishing because it takes so long for those sharks to rebound and regrow their populations,” McCauley said
Other marine animals at risk in the monument are sea turtles. With six of the global seven sea turtle species being classified as threatened or endangered worldwide due to human activity
many come into the islands to feed around the reefs
Trump’s proclamation puts them at risk in various ways
with McCauley saying: “Either they take a hook and bite on to the hook or drown because they cannot come up to breathe in a longline fishery
or they are scooped up and drown in the course of purse-seine fishing.”
a Hawaiian elder and leader with the Pacific Island Heritage Coalition
pointed to the interconnectedness of the islands to the broader ocean
View image in fullscreenA blacktip reef shark swims in Palmyra Atoll. Photograph: Shark Stewards“It’s an integrated kind of ecosystem that isn’t isolated by just the islands themselves … It’s difficult to think that we can divide them into separate areas and then be successful in preserving all of them. It doesn’t work that way,” he said.
For environmental experts, in addition to fragile ecosystems, Trump’s proclamation will negatively impact American fishers in the long run, leading to higher seafood prices for American consumers.
Read moreResearch has repeatedly shown spillover benefits from large marine protected areas including increases in catch rates outside of the areas
Opening up the monument for commercial fishing will have what Hemphill describes as the “opposite effect” of what Trump’s administration hopes for
“The current administration has its mentality of ‘let’s become the greatest seafood producer.’ But if you take everything
then you over-exploit and the populations collapse
Then what you’ll see in the long term is actually a reduction of catch,” he said
Similarly, Kaho’ohalahala said: “Opening this sacred place for exploitation is short-sighted and does not consider current or future generations of Pacific People who rely on a healthy ocean
and know this special ocean space as our ancestral home.”
With mounting concerns surrounding the Trump administration’s environmental impact
marine experts are urging the public to consider the ecological and cultural significance of marine regulated areas that are akin to national parks
“It’s a special piece of America… It’s as if we had just allowed commercial hunting into a place like Yellowstone,” McCauley said
As Ningaloo reef bleaches and an election looms
we must hold to account those who stand in the way of our safety – the small cohort profiting from fossil fuels
Late last spring, I was part of an expedition to Scott Reef, a magnificent coral atoll nearly 300 kilometres off the Kimberley coast. And while it was a privilege to be in such a remote and wonderful place, watching rare and endemic sea life drifting past, the moment I tipped from the boat in my mask and fins, I knew something was wrong.
The water was too hot. Not tropical warm, but uncomfortably hot.
Our first dive was over a coral garden at the crest of a sea mount. But I struggled to concentrate on what I was seeing, because of an uncanny, skin-crawling sensation that came over me at the surface. When I took a breath and got down past 8 metres, the unpleasantness receded a little, but on the way back up it overtook me like the shimmery, woozy feeling you get before you faint.
“Is it just me,” I asked marine ecologist Dr Ben Fitzpatrick as we climbed back into the dinghy, “or is this water super hot?”
The veteran marine scientist pointed to the boat’s sonar unit. The reading it gave was 35C.
1:27Footage shows coral bleaching at Western Australia's Ningaloo Reef – videoOur next dive was in the idyllic lagoon near Sandy Islet. As outgoing tide drained the shallows, the water grew pearly, almost opaque, like what comes out of the hot tap at home. Where the current drove down into the deep drop-off, the thermocline was visible – you could see the hottest water colliding with the cooler layers. At the surface, it was 36C.
“Dear God,” I said. “It’s only November. Is this just a local anomaly?”
Read moreThe way Ben dropped his mask at his feet and looked away to the horizon was not at all reassuring
I told myself the boat’s instruments were a little off kilter
Ben brought up the sea temperature satellite models on his laptop
“You know where all this hot water is headed
The Leeuwin current pushes south and drives tropical water inshore along the West Australian coast
The dread in that moment of recognition haunted me for the remainder of the trip
In December, we heard the first reports of corals bleaching in the Kimberley. Farther south, in January, 30,000 fish died en masse on the Pilbara Coast
Last week, Ningaloo reef began to experience widespread coral bleaching
Early reports had sea temperatures 4 degrees hotter than usual
View image in fullscreen‘These are not just unseasonable temperatures – they are unsafe
and they’re humanly unsustainable.’ Coral bleaching on Ningaloo reef
Photograph: Violeta J Brosig/Blue Media ExmouthAs Ningaloo’s many gifted photographers and videographers began to document the reef’s distress
Coming so hard on the heels of the bleaching episode of 2022
Some cling to the hope that things look worse than they are
Those of us who’ve been studying and defending Ningaloo for decades are trapped between rage and sorrow
Because we know this was a foreseeable calamity
This is what 30 years of denial and delay have brought us
This is what current government policy settings produce
and what they’ll continue to inflict on our coral reefs unless we turn back from the brink right now
These marine heatwaves are becoming more frequent and more intense
politicians and fossil fuel barrackers dismissed their warnings
Such is the cost of business as usual – more heat stress
Winter temperatures in the north of WA were in the 40s last year
Over summer they’ve been in the high 40s for days on end
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These are not just unseasonable temperatures – they are unsafe
We should not be expected to find them politically acceptable
We are on track for 3C of heating
Which means all coral reefs will die and vast swathes of the planet will become uninhabitable
The IPCC says that if we can restrict heating to 1.5C
and fewer humans would perish or be forced to live in misery
But to do this we’d need to refrain from any more fossil fuel developments
That means putting humanity’s long-term wellbeing first
The science is clear on this – the morality should be too
Elections aren’t our only opportunity to disrupt and destroy business at usual
but they’re a good place to beginThe problem is
that a small cohort of people make enormous
and the political leaders who protect their commercial interests
all deny responsibility for climate breakdown
yet their role in delivering all this heat and suffering is clear and unequivocal
These are the people who stand in the way of our safety
with two significant elections ahead of us in WA
while we’re still absorbing the week’s bad news from Ningaloo
Having acknowledged our extinction crisis and the climate emergency
Anthony Albanese promised to introduce more effective nature laws
His government hasn’t delivered on that promise
A policy failure this monumental isn’t just politically embarrassing – in the real world of blood and fur and feathers
Sad to say, part of that shame can be sheeted home to my home state of Western Australia. The last-minute intervention of our premier, Roger Cook
ensured the extinction of those new nature laws
we should be sure to identify its sources and use that knowledge to bring about change
Tim Winton is an Australian novelist. His new novel Juice is out now
Metrics details
Recent discussions have raised concerns about the long-term effectiveness of coral reef restoration efforts
questioning whether current interventions can effectively address the ongoing loss of reef ecosystems
details matter and vary greatly with respect to scale
and diverse approaches are needed to maintain functional coral reef ecosystems
Prices may be subject to local taxes which are calculated during checkout
Maragos, J. E. Coral Transplantation: A Method to Create, Preserve, and Manage Coral Reefs (NOAA, 1974); https://go.nature.com/3YFGpZt
Williams, D., Nedimyer, K., Bright, A. & Ladd, M. Genotypic Inventory and Impact of the 2023 Marine Heatwave on Acropora palmata (Elkhorn Coral) Populations in the Upper Florida Keys, USA: 2020–2023 (NOAA, 2024); https://doi.org/10.25923/37c0-x182
Rebuilding Coral Reefs: A Decadal Grand Challenge (International Coral Reef Society and Future Earth Coasts
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Villela for her insights and support with the figures
These authors contributed equally: Raquel S
Division of Biological and Environmental Science and Engineering (BESE)
King Abdullah University of Science and Technology (KAUST)
Helmholtz-Institute for Functional Marine Biodiversity at the University of Oldenburg (HIFMB)
Helmholtz-Centre for Polar and Marine Research (AWI)
Institute for Chemistry and Biology of the Marine Environment (ICBM)
School of Natural and Environmental Sciences
Instituto de Ciencias del Mar y Limnología
King Abdullah University of Science and Technology
Australian Institute of Marine Science (AIMS)
While no competing interests exist for any of the manuscript’s authors
the following information is provided for the sake of full transparency
are members of the science advisory board for SECORE International
are members of the advisory board for the Coral Restoration Consortium (CRC)
community of practice for reef restoration
is the CRC advisory board chair and senior reef strategy lead at The Nature Conservancy
board member of the CRC and founder of GCS
Smith is the senior director of Mars Sustainable Solutions
and chief science advisor to the MSF Foundation
are the co-founders of Coral Nurture Program
K.E.F.’s research is co-funded by the Reef Restoration and Adaptation Program
a partnership between the Australian Government's Reef Trust and the Great Barrier Reef Foundation
The positions of all co-authors are based on their expertise and remain unbiased
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DOI: https://doi.org/10.1038/s41558-024-02202-z
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Researchers have discovered a rare example of ‘great fish parenting’ with a common coral reef species found to actively protect their young by eating parasites
The University of Queensland’s Dr Alexandra Grutter said the team identified that a species of damselfish cared for their offspring and improved their chances of survival by eating the parasitic gnathiid isopods
“In the marine environment the care of fish eggs is common
but caring for the tiny larval fishes after they hatch is rare,” Dr Grutter said
“In most cases the larvae leave the reef for the open ocean
spiny chromis damselfish offspring found in the western Pacific Ocean never leave the reef and are cared for by both parents.”
The researchers discovered the parent fish actively eat gnathiids
which are common reef parasites that feed briefly on the blood of their host and leave when full
“From our previous research we know gnathiids are especially harmful to juvenile fishes by reducing their swimming
aerobic performance and overall survival,” Dr Grutter said
The study was conducted by adding cultured parasites to two aquariums of juvenile fish – one tank with a parent fish and the second without a parent – and recording what happened over 3 days
The survival rate of the juvenile fish in the tank with a parent was 3 times higher than those without a parent fish
The researchers said further tests in the laboratory and in the ocean confirmed the parent fish were defensively eating gnathiids
“We are now interested to learn how other young fishes without such parental care avoid suffering from gnathiid parasitic infection,” Dr Grutter said
While parasite-removal services are often provided by ‘cleaner fish’
“Given how tiny the damselfish offspring are
these fish parents have really come to the rescue,” Dr Grutter said
“We will be keen to see if there are other examples of fish showing parental care involving the consumption of parasites.”
Metrics details
a consequence of stressed symbiotic relationships between corals and algae
has escalated due to intensified heat stress events driven by climate change
current early warning systems lack local precision
spanning 2015–2017 in the Mesoamerican Reef
By scrutinizing 23 stress exposure and sensitivity metrics
we accurately predicted 75% of bleaching severity variation
distinct thermal patterns—particularly the climatological seasonal warming rate and various heat stress metrics—emerged as better predictors compared to conventional indices (such as Degree Heating Weeks)
deeper reefs with diverse coral communities showed heightened vulnerability
This study presents a framework for coral reef bleaching vulnerability assessment
leveraging accessible data (including historical and real-time sea surface temperature
Its operational potential lies in seamless integration with existing monitoring systems
offering crucial insights for conservation and management
an accurate prediction of the vulnerability of bleaching is a critical aspect of the management and applied conservation of coral reefs
there are no predictive frameworks designed to evaluate the cumulative effects of consecutive heat stress events or to allow the additive inclusion of other stressors that can help explain the spatial variability of coral bleaching events
Our results uncovered the additive effect of seven metrics to explain ~75% of the variation of coral bleaching severity
we propose a model to predict coral reef vulnerability to bleaching
with a high potential for use as an early warning system for the Mesoamerican Reef transferable to other ecoregions in the wider Caribbean
It can also be used to predict reefs with intrinsically more resistance to bleaching for conservation planning purposes
The operational use of our model is facilitated by the accessibility of essential data sources
including historical and actual sea surface temperature data
These readily available datasets enable efficient implementation and integration into existing monitoring systems
providing valuable insights for coral reef conservation and management efforts
a Distribution of the bleaching severity index (BSI) values and the proportion of colonies in each bleaching category, each year, for all the reefs sampled. Information on the BSI’s statistical descriptors and the categories defined for coral bleaching can be found in Supplementary Table 1
b Maps illustrate the spatial distribution of the severity of coral bleaching in each year
Considering the existing evidence and the results obtained in this analysis
we conclude that not only the current thermal regime but also the history of heat stress of a particular reef needs to be considered to predict the risk of bleaching during a new event
and recent history of exposure to heat stress is fundamental for the prediction of coral bleaching during long-lasting events
The figure shows only the species with more than 500 colonies assessed during the entire period (2015–2017). The information on the overall impact observed on each species is shown in Supplementary Table 4
more diverse reefs could have more abundance of different sensitive species
Our results then stress the relevance of multiple metrics and the integration of different approaches (i.e.
and ecological surveys) to fully understand the range of coral responses to heat stress and the risk of bleaching on a particular reef
The understanding of why shallower reefs with lower diversity could be less vulnerable to bleaching
or how they handle high environmental variability or form more resistant coral communities after surviving greater past disturbances (ecological filters)
requires a complex and integrative approach
Conceptual diagram of an early warning system for predicting coral bleaching vulnerability within a regional framework
heat stress metrics from remote sensing data
and biophysical descriptors (species composition
Positive and negative relationships with bleaching severity are indicated by upward and downward arrows
The right panels describe the implementation process
and the system's ability to improve accuracy through new information
Corals were identified at the species level and assessed using three bleaching categories: pale colony
and whole colony bleached with over 90% of live tissue affected; and one category for non-affected colonies
Sampling was conducted throughout the whole MAR region in three periods: October–November 2015
Sites were selected based on information from previous monitoring programs in the region
Site selection was stratified according to cross-shelf position (e.g.
Most of the selected sites had consistent information in other regional databases (e.g.
Atlantic Gulf and Rapid Reef Assessment-Healthy Reefs Initiative
and we prioritized areas based on the experience and feasibility of the surveys achieved by local experts
The monitoring was conducted by trained volunteers from various partner institutions of the Healthy Reefs Initiative within Mexico
266 reef-level samples/observations were obtained: 69 in 2015
weighting each category according to its ecological impact
‘n’ corresponds to the total number of colonies
and ‘c’ represents the number of colonies in each of the categories of concern (c2: pale
Bleaching severity was calculated for each of the reefs and each of the species considering all the colonies of each species
Five different metrics were calculated to describe the sensitivity of corals to bleach, based on species composition and reef diversity (Table 1)
The first step in obtaining these indicators was the selection of the database
including only the colonies identified at the species level
When species had no functional coefficient
the value available for congeners was used (e.g.
Solesnatrea hyades was used for Solenastrea bournoni)
Colonies were not considered when a value for the species could not be assigned (i.e.
This diversity indicator considers both the richness or number of species (s)
as well as the proportion or relative abundance of each species (pi)
maximum monthly mean (MMM) values were obtained from the same database
this metric provides information on the relative magnitude of the heat stress event as a function of the previous year’s exposure
Further information on research design is available in the Nature Portfolio Reporting Summary linked to this article
All source data underlying the graphs and charts presented in the main figures of this study are available as Supplementary Material and Supplementary Data 1–2
These data include detailed site-specific metrics on coral bleaching severity
and species composition used in the analyses
The complete datasets generated during and/or analyzed during the study are available from the corresponding author upon reasonable request
Spatial and temporal patterns of mass bleaching of corals in the Anthropocene
The 2014–2017 global-scale coral bleaching event: insights and impacts
Temperature patterns and mechanisms influencing coral bleaching during the 2016 El Niño
Global warming and recurrent mass bleaching of corals
Marked annual coral bleaching resilience of an inshore patch reef in the Florida Keys: a nugget of hope
Ecosystem restructuring along the Great Barrier Reef following mass coral bleaching
Bleaching drives collapse in reef carbonate budgets and reef growth potential on southern Maldives reefs
Global warming impairs stock–recruitment dynamics of corals
Redefining thermal regimes to design reserves for Coral Reefs in the face of climate change
Beyer, H. L. et al. Risk-sensitive planning for conserving coral reefs under rapid climate change. Conserv. Lett. https://doi.org/10.1111/conl.12587 (2018)
Darling, E. S. et al. Social–environmental drivers inform strategic management of coral reefs in the Anthropocene. Nat. Ecol. Evol. https://doi.org/10.1038/s41559-019-0953-8 (2019)
robustness and vulnerability: how do these concepts benefit ecosystem management
Caribbean corals in crisis: record thermal stress
Treating coral bleaching as weather: a framework to validate and optimize prediction skill
High frequency temperature variability reduces the risk of coral bleaching
Coral responses to climate change exposure
Climate change disables coral bleaching protection on the Great Barrier Reef
Ecological memory modifies the cumulative impact of recurrent climate extremes
Emergent properties in the responses of tropical corals to recurrent climate extremes
A global analysis of coral bleaching over the past two decades
Coral bleaching response index: a new tool to standardize and compare susceptibility to thermal bleaching
Coral bleaching indices and thresholds for the Florida Reef Tract
The role of zooxanthellae in the thermal tolerance of corals: a ‘nugget of hope’ for coral reefs in an era of climate change
Microbial invasion of the Caribbean by an Indo-Pacific coral zooxanthella
Multiple scattering on coral skeletons enhances light absorption by symbiotic algae
Changes in the number of symbionts and Symbiodinium cell pigmentation modulate differentially coral light absorption and photosynthetic performance
Key functional role of the optical properties of coral skeletons in coral ecology and evolution
Seasonal variation modulates coral sensibility to heat-stress and explains annual changes in coral productivity
Coral bleaching: the winners and the losers
Bongaerts, P., Ridgway, T., Sampayo, E. M. & Hoegh-Guldberg, O. Assessing the ‘deep reef refugia’ hypothesis: focus on Caribbean reefs. Coral Reefs https://doi.org/10.1007/s00338-009-0581-x (2010)
Drivers of coral bleaching in a Marine Protected Area of the Southern Gulf of Mexico during the 2015 event
Bleaching susceptibility and recovery of colombian caribbean corals in response to water current exposure and seasonal upwelling
Estimating the effect of multiple environmental stressors on coral bleaching and mortality
A strategic framework for responding to coral bleaching events in a changing climate
Reef-scale thermal stress monitoring of coral ecosystems: New 5-km global products from NOAA coral reef watch
ReefTemp: an interactive monitoring system for coral bleaching using high-resolution SST and improved stress predictors
Prediction of coral bleaching in the Florida Keys using remotely sensed data
Three decades of heat stress exposure in Caribbean coral reefs: a new regional delineation to enhance conservation
A working guide to boosted regression trees
Hastie, T., Tibshirani, R. & Friedman, J. The Elements of Statistical Learning: Data Mining, Inference, and Prediction, Second Edition. Springer Series in Statistics https://doi.org/10.1007/978-0-387-84858-7 (2009)
Identifying multiple coral reef regimes and their drivers across the Hawaiian archipelago
The relationship between bleaching and mortality of common corals
Coral response during and after mass bleaching in Belize
Century-scale records of coral growth rates indicate that local stressors reduce coral thermal tolerance threshold
Baumann, J. H. et al. Nearshore coral growth declining on the Mesoamerican Barrier Reef System. Glob. Chang. Biol. https://doi.org/10.1111/gcb.14784 (2019)
Sully, S. & van Woesik, R. Turbid reefs moderate coral bleaching under climate-related temperature stress. Glob. Chang. Biol. https://doi.org/10.1111/gcb.14948 (2020)
Climate change and coral reef bleaching: an ecological assessment of long-term impacts
Nutrient enrichment can increase the susceptibility of reef corals to bleaching
Coral reefs under rapid climate change and ocean acidification
Do fluctuating temperature environments elevate coral thermal tolerance
Influence of thermal history on the response of Montastraea annularis to short-term temperature exposure
Historical temperature variability affects coral response to heat stress
coral bleaching and the future of the world’s coral reefs
Coral bleaching pathways under the control of regional temperature variability
Marine heatwave hotspots in Coral Reef environments: physical drivers
Coral host transcriptomic states are correlated with Symbiodinium genotypes
Experimental evidence for high temperature stress as the cause of El Niño-coincident coral mortality
Heterotrophic plasticity and resilience in bleached corals
The cumulative impact of annual coral bleaching can turn some coral species winners into losers
Annual coral bleaching and the long-term recovery capacity of coral
Photosynthesis and light utilization in the Caribbean coral Montastraea faveolata recovering from a bleaching event
Major bleaching events can lead to increased thermal tolerance in corals
Bleaching response of coral species in the context of assemblage response
Comparing environmental influences on coral bleaching across and within species using clustered binomial regression
Contrasting patterns of coral bleaching susceptibility in 2010 suggest an adaptive response to thermal stress
Widespread loss of Caribbean acroporid corals was underway before coral bleaching and disease outbreaks
Diversity of symbiotic dinoflagellates (zooxanthellae) in scleractinian corals of the Caribbean and Eastern Pacific
A framework for measuring coral species-specific contribution to reef functioning in the Caribbean
The rarity of depth refugia from coral bleaching heat stress in the Western and Central Pacific Islands
When depth is no refuge: cumulative thermal stress increases with depth in Bocas del Toro
Caribbean mesophotic coral ecosystems are unlikely climate change refugia
Diversity in Tropical Rain Forests and Coral Reefs
The influence of species diversity and stress intensity on community resistance and resilience
Reciprocal relationships and potential feedbacks between biodiversity and disturbance
Influence of water-temperature variability on stony coral diversity in Florida Keys patch reefs
Validation of Reef-scale thermal stress satellite products for coral bleaching monitoring
Detrended correspondence analysis: an improved ordination technique
R. Core Team. R: A language and environment for statistical computing. R Foundation for Statistical Computing Vienna Austria. https://doi.org/10.1038/sj.hdy.6800737 (2017)
Skirving, W. J. et al. The relentless march of mass coral bleaching: a global perspective of changing heat stress. Coral Reefs https://doi.org/10.1007/s00338-019-01799-4 (2019)
Mair, P. & Wilcox, R. R. Robust Statistical Methods Using WRS2. J. Stat. Softw. https://doi.org/10.18637/jss.v000.i00 (2017)
Package ‘gbm’ - Generalized Boosted Regression Models
Package ‘dismo” - Species Distribution Modeling’
Collinearity: a review of methods to deal with it and a simulation study evaluating their performance
A protocol for data exploration to avoid common statistical problems
Download references
The authors also thank the NOAA Coral Reef Watch program for the availability of the SST data
program of AIMC in the postgraduate program of Marine Science at CINVESTAV
This program is acknowledged for providing four years of a CONACYT fellowship with grant numbers 340074 and 666908 to support the Ph.D
Special thanks to the Coastal Biodiversity Resilience to Increasing Extreme Events in Central America (CORESCAM) research project
as well as any views or opinions expressed herein
are those of the authors and do not necessarily reflect the views of sponsoring organizations
Laboratorio de Ecología de Ecosistemas de Arrecifes Coralinos
Centro de Investigación y de Estudios Avanzados del Instituto Politécnico Nacional
Andrea Rivera-Sosa & Jesús Ernesto Arias-González
Unidad Académica de Sistemas Arrecifales Puerto Morelos
managed planning and funding for fieldwork
coordinating the coral bleaching monitoring response plan
developed the study concept and analytical framework
carried out the statistical analyses and figures with contributions from A.R.S.
led the writing with contributions from all authors
Communications Biology thanks Daniel Barshis
anonymous reviewer(s) for their contribution to the peer review of this work
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DOI: https://doi.org/10.1038/s42003-024-07128-y
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law and environmental management to enable graduates to strategically address human challenges in ocean systems and to implement solutions for the future of our coasts and seas
The Industrial Transformation Research Hub for Offshore Floating Facilities (OFFshore ITRH) is a multi-disciplinary research initiative jointly funded by industry and the Australian Research Council
OFFshore ITRH are collaborating on the critical engineering challenges faced by offshore oil and gas projects by creating improved design and operating procedures
The team are based at the University of Western Australia
with nodes at Western Sydney University and The University of Southampton
Find out more
The Wave Energy Research Centre (WERC) in Albany
was built to look at ways we can generate renewable energy from our oceans on an industrial scale
Find out more
The Centre for Offshore Foundation Systems (COFS) is a world-leading research facility used to examine offshore geomechanics and engineering
Find out more
The ARC Centre of Excellence for Coral Reef Studies undertakes world-best integrated research for sustainable use and management of coral reefs
Find out more
The UWA Oceans Institute delivers research and training to students and partners
working to ensure what we investigate has maximum impact
As a multidisciplinary marine research organisation
and how these themes tie in with the ocean
The Oceans Institute is the forefront of ocean science and technology knowledge
providing a focal point for Indian Ocean researchers to collaborate and share ideas
The greatest minds in marine and ocean biology are collaborating at our world-leading facilities
The Oceans Graduate School has a range of partnerships with local
national and international organisations and bodies
Christophe is a Professor of Geotechnical Engineering at the University of Western Australia
He is the Director of the newly established Wave Energy Research Centre in Albany and the Head of the Oceans Graduate School
a multi-disciplinary research group of about 100 oceanographers
Christophe graduated with a Doctorate in Soil Mechanics from the Ecole Centrale de Nantes in November 2002
and joined the University of Western Australia in July 2003
His research interests cover offshore anchoring systems and shallow foundations
pipeline-soil interaction and similitude principles associated with centrifuge modelling
for which he has authored over 180 referred publications
He is currently spearheading several research initiatives associated with foundation systems for offshore renewables
with support from local and international industry
Level of engagement with Universities / Academia
Christophe has undertaken over 50 research contracts with industry over the last 15 years associated with oil and gas developments all around the world
and used to consult for Advanced Geomechanics
He is a strong advocate of close collaboration between universities and industry to better train students
inform research and optimise impact and outcomes and develop relevant support and services
Dave has been working in the oil industry for over 18 years
Dave is currently the Director of Consulting for Granherne / KBR in Perth
Previously Dave was the engineering manager for Shell seconded into Arrow Energy in Queensland where he ran all engineering and design work on all of their upstream developments
Dave has also led all deep water development and engineering work for Shell In Perth
participated in 4 mega-project FIDs in Western Australia and worked in offshore operations in Australia and the North Sea
Dave holds a Master’s Degree in Engineering from Gonville and Caius College
and is a chartered Electrical and Petroleum engineer and a Fellow of Engineers Australia
Dave is an adjunct Professor of Chemical Engineering at the University of Queensland and the Chairman of the Industry Advisory Board to the Oceans Graduate School at UWA
Dave helped set up Shell’s involvement with UWA
Dave has actively participated in linking universities and Industry in both WA and QLD
David is keen to see Granherne / KBR lead the way in contractor engagement with universities and actively participate in their work as there are huge wins for both organisations from working together.
Graduated from Southampton University in 1982 with an Honours Degree in Ship Science
Has 25 year’s experience with the Lloyds Register Group (LR) as Project Manager for new construction Validation
Classification and Certification Services Contracts
dealing with Fixed and Floating Offshore Installations
Jeff relocated from London to Perth in early 2004 to manage LR’s involvement in the Woodside Enfield Project and subsequently the Angel and Vincent Projects
In 2008 he was appointed Oil and Gas Business Manager for Australasia
Following the merger of LR's Oil and Gas Compliance and Marine businesses
Jeff is currently Offshore Business Development Manager for Australasia
covering all onshore and offshore compliance services to the Oil and Gas industry in the region
Jeff is a UWA FOI ITRH Board Member for Lloyds Register Group
represents the Lloyds Register Foundation in their ongoing support of the UWA COFS team and is focal point for miscellaneous other initiatives with the UWA team
Jill is founder of a small boutique agency setup to support industry-research engagement
Previously she was the GM for industry-research and innovation at NERA
Deputy Director of the UWA Energy & Minerals Institute
Deputy Director of the International Mining for Development Centre
CEO of the Science Teachers Association and CEO of the International Association of Teachers as a Foreign Language
Passionate about economic development and especially keen to see women in high-value STEM roles
Jill is a Director on the Commercialisations Studies Centre Board
an IMNIS mentor and Read Write Now volunteer
Jill has been associated with the university and research sector for the past 10 years in an energy business development role
she helped secure over $80M during this time for academic research and infrastructure
is supporting the setup of a UWA Industry 4.0 digital interoperability laboratory for process control
she is supporting a Cooperative Research Centre bid for Future Energy Exports and an automation centre in Karratha
Jill is a passionate supporter of the university sector and in particular research engagement with industry
Luke is the CEO of the Western Australian Marine Science Institution (WAMSI)
a joint venture made up of 14 partners with the objective to maximise the sustainable environmental
economic and social benefits from Western Australia’s marine estate by enabling outcome focussed marine science
Luke was a Director and Principal Consultant for BMT Oceanica
a specialist marine environmental consultancy
Luke worked on developing EIA and compliance assessment of capital dredging programs such as the Oakajee Deepwater Port
Albany Port Expansion Project and Post-Development Surveys for the Chevron Australia Gorgon Project
Luke was also the first Principal Scientist for the Swan River Trust
where he utilised his knowledge of phytoplankton ecology developed from his PhD at Curtin University and Postdoctoral position at the University of North Carolina at Chapel Hill
Luke holds adjunct Associate Professor positions at Murdoch University and Curtin University.
Through the WAMSI partner membership with Curtin
Luke has a strong connection with Western Australian universities and academics
WAMSI has engaged Industry stakeholders in the development of long-term strategy for marine science in Western Australia through the Blueprint for Marine Science
In his previous role as a Principal Consultant and Director at BMT Oceanica
Luke often engaged specialists from the universities to assist with aspects of environmental impact assessment on major infrastructure projects for Oil and Gas and Port sectors
Luke is a strong advocate of student programs in applied marine science
Sean graduate with a BSc in Marine GeoTechnics & an MSc in Subsea Engineering in 1989
He has worked in the Oil & Gas Industry for 30 years
predominantly in Subsea & Pipeline Engineering & Project Management (Design
Construction and Operations); spending 15 yrs
Brazil and West of Africa before moving to Western Australia to join Woodside
Since 2004 Sean has been responsible for developing Woodside’s Subsea & Pipeline capability and infra-structure before moving to VP Technology in 2015 and recently; VP Remote Operations
Woodside has a very strong and broad relationship with UWA across many faculties
Sean has been engaged directly in ‘O-Tube’ & Flow Assurance activities and more broadly in the FutureLab (Oceanworks & RiverLab) initiatives at UWA
Sean has also been involved in equivalent FutureLab initiatives at Curtin and Monash Universities
all designed to encourage and stimulate collaboration and enhanced industry / academic interactions
Hatton has served as Chairman of the Western Australian Environmental Protection Authority since 2015
He holds a Bachelor of Science and Master of Science from Humboldt State University
and a doctorate from the College of Natural Resources at Utah State University
Following post-doctoral studies in mathematics at the University of New South Wales he joined the CSIRO as an environmental scientist
working on the many water-related challenges facing Australia. Over a 25-year career at the CSIRO
Tom received the CSIRO Chairman’s Medal and the Australian Public Service Medal for his contributions to the management of Australia’s water resources
and was made a Fellow of the Australian Academy of Technology and Engineering in 2017
He is an adjunct professor at the University of Western Australia and serves on the Boards of the Oceans Institute
the International Centre for Radio Astronomy Research and the Western Australia Parks Foundation.
Pru Ayling is currently Industry Engagement Manager at the University of Western Australia and is responsible for enabling key university initiatives in defence
Pru has worked in WA State Government for over ten years and has been responsible for a range of key strategic state initiatives
innovation and the Australian Marine Complex
Pru works in multi-disciplinary projects across UWA and facilitates sustainable partnerships with industry and the University
Stuart Smith was appointed CEO of the National Offshore Petroleum Safety and Environmental Management Authority (NOPSEMA) in September 2014; Australia’s independent regulator of offshore safety
well integrity and environmental management of offshore oil and gas facilities around Australia
Stuart spent six years as Director General for the Department of Fisheries in Western Australia (WA) with responsibilities for managing aquatic resources in federal and state waters
Stuart also worked with the Department of Industry and Resources in WA as Acting Director General and a Deputy Director General
he had responsibility for facilitating international trade and investment
negotiating major state development projects and regulating the resources sector
including onshore and offshore oil and gas safety and environmental management
Before joining the WA Public Service in 2003
Stuart spent 14 years with the Australian Public Service in Canberra
During this period he held various industry development and regulatory roles including positions with the Industry portfolio and the Australian Competition and Consumer Commission
Stuart holds a Bachelor of Economics from the University of Western Australian and a Graduate Diploma in Economics from the Australian National University
The Great Southern is one step closer to becoming a global leader in marine renewable energy after the Albany Visitor Centre was announced as the location for the Wave Energy Research Centre after the State Government awarded $3.75 million to The University of Western Australia
Scientists from the ARC Centre of Excellence for Coral Reef Studies (Coral CoE) at The University of Western Australia (UWA) have found that some corals are able to combat the effects of ocean acidification by controlling their own chemistry
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The University of Western Australia acknowledges that its campus is situated on Noongar land
and that Noongar people remain the spiritual and cultural custodians of their land
Indigenous commitment
Dive into your beach vacation with reef safe sunscreen that protects your skin and the ocean
Reef safe sunscreens are mineral-based and avoid harmful chemicals that can leech into the water
Oxybenzone and octinoxate are the main ingredients you want to avoid
but you should also look for mineral-based sunscreens that use non-nano zinc or non-nano titanium (too small
You should also avoid ingredients including homosalate
It has a creamy-smooth application and protects your skin even in intense
It leaves a light white cast for about one minute after applying
With tinted and nontinted options to choose from
it’s easy to add this sunscreen to your daily routine
It needs to be reapplied after 40 minutes in the water
You don’t need to reapply for up to four hours
depending on your skin needs and sun exposure
It has a thicker texture than standard sunscreens
reef safe products may need to get used to the feel
The stick is easy to use and allows you to apply sunscreen without getting sticky (or sandy)
It leaves a white cast for about 15 minutes after application
It’s lightweight and blends easily without any skin irritation
The lotion sunscreen only goes up to SPF 30
protective sunscreen does not leave your skin feeling greasy or waxy
It has “no added fragrance,” but it does have a light citrus smell
You can wear this under makeup or on its own for daily protection that doesn’t run or pill
It blends into the skin like a standard moisturizer and does not leave a white cast
so you may want to pack it inside a plastic bag to prevent spills
It’s lightweight and can be worn under makeup or as a standalone product
It has a peachy color that may be difficult to blend in
They are generally made with zinc oxide and titanium dioxide
which sit on top of the skin as opposed to absorbing into the skin
Standard sunscreens utilize oxybenzone and octinoxate
which have a tendency to leech off into the water
will also utilize non-nano zinc or titanium
Reef safe sunscreens also do not utilize exfoliating beads
The terms “reef friendly” and “reef safe” are not regulated; however
we have noticed that many sunscreens use the term “reef friendly” when their packaging is recyclable
but they may still include nano zinc or nano titanium
Look for non-nano zinc or titanium for a safer
The SPF level you use really depends on your skin type
SPF 30 is a good level for daily protection
you want to make sure to prioritize the time for effective water-resistance
I know I’ll be in the water for no less than one hour
so I need to prioritize a sunscreen that lasts at least 60 minutes (but 80+ is ideal)
you’re still very exposed to the sun’s rays
so you may also consider wearing a rashguard or wetsuit for optimal protection.