Coral Reef Diagnostics

Saudi Red Sea - Shark Reef (Thuwal)

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05
Photo: Anderson Mayfield/Coral Reef Diagnostics
Survey date(s)
2024-08-31
2024-09-14
Coordinates
22.4317, 38.9969
Coral cover
16%
Published point count (Mayfield 2025; CoralNet-assisted, 421 photos) · details below
Coral bleached
72%
of coral tissue · Mayfield (2025), Environments 12:248
Heat stress
Most recent heat load record
26 Oct 2026 · Alert Level 2
5-year thermal stress load
5-year mean max. degree heating weeks (DHW)
2021–2025
NOAA Coral Reef Watch — Al Madinah and Makkah virtual station
i 5-year mean max. DHW is the mean of the annual maximum DHWs over the five complete years named above, not conditions today.
More infoAl Madinah and Makkah (NOAA CRW virtual station)
Photographs
442
24 shown on this page
Site summary
Read this summary in:

At Shark Reef, two visits at the peak of the 2024 bleaching event found roughly seven in ten corals bleached (73% and 71% of tissue), with whole slope faces of massive Porites, other massives, and Acropora glowing uniform white in frame after frame, plus three crown-of-thorns starfish photographed amid the dying reef. Anderson's field notes from the dives, which record severe bleaching, dead corals, and a dying reef, match what the images show; cover itself held around 16%, since bleached-but-alive coral still counts as cover.

Max. depth dived
32.4 m
dive-log maximum
Water temp. during survey
31–33°C
Published dive temperature (Mayfield 2025, Environments 12:248, Appendix A): 33°C on 31 August and 31°C on 14 September 2024.

Three independent survey stations shown with the program’s logo — click one to see how far it is from this site.

11 of the 24 photographs on this page are shown beside the text that discusses them under "Site description" below.

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Photo credit & attribution

Site description

General benthic features

The reef is a steep buttressed slope of large massive corals — knobby and columnar Porites and other domed and encrusting massives — over consolidated pavement, with pocilloporids and branching Acropora in the shallows and undercuts holding bluestripe snapper and moray eels (e.g., Image 2, Image 5).

Coral cover

Stressors

The photographs leave no room for interpretation. In wide-angle frame after wide-angle frame the dominant color is white: whole slopes where the majority of visible colonies are stark, uniform, glowing white from top to bottom, running out of the frame in both directions (e.g., Image 3, Image 8, Image 9).

Anderson's field notes for this dive record severe bleaching; bleached pocilloporids, corals, and anemones; bleaching Porites; and dead and dying coral, among it dead Acropora, a mostly dead acroporid, pocilloporids that were nearly dead or dead, and dead coral covered in algae. And there are crown-of-thorns here: three separate Acanthaster individuals photographed amid bleached and dying coral, one on 31 August and two different ones on 14 September, a gray-green one on open rubble (e.g., Image 1) and a reddish-brown one in a crevice among bleached massives.

Pink-lavender colonies in Anderson's frames from both days (e.g., Image 21, Image 18), including one noted as a nearly dead pocilloporid (e.g., Image 22), are fluorescent (colorful) bleaching.

In one 14 September frame a rust-orange cyanobacterial mat is overgrowing dead coral framework (e.g., Image 23).

Fish and other fauna

Two giant clams sit among bleached colonies (e.g., Image 5), and a blue-spotted stingray was photographed on the 14 September dives (e.g., Image 24).

Comparisons with other data

Aeby et al. (2021) surveyed a nearby station (Qita al Kirsh) in 2015, 0.36 km from the pin. Within 5 km, three independent stations recorded station-year means of 23–60% hard coral cover between 2010 and 2015; the nearest, Monroe et al. (2018) at Midshelf reef 2, 0.36 km away, read 37% in 2015.

Dive record

Two logged dives on 14 September 2024 (the 31 August visit is not in the log) at the peak of the 2024 Red Sea bleaching event, worked with Coastline (KAUST).

Survey summary

Shark Reef: surveyed 2 times, Aug 2024–Sep 2024 (CoralNet point counts; Mayfield 2025, Environments 12:248). Surveyed in partnership with Coastline (KAUST).

CV model comparison

Computer-vision estimates from this site's own photographs are listed in the comparison table below, alongside the headline rather than merged into it.
Headline is the reference value; every other row is listed beside it for comparison and none is averaged in.
More infoThe reference is this dive site's own published CoralNet point count by the author (Mayfield 2025, Environments 12:248, Appendix A; most frames annotated by CoralNet's AI, trained and checked by the author). The computer-vision rows are this site's own values: Claude is a blind point count of all of the site's edited photographs, and CoralSCOP is the site's finished survey of its edited photographs. They are on different frame sets from the published count, a row under 30 frames is indicative only, and no computer-vision method yet estimates coral cover accurately on new images.
MethodHard coral cover (%)Photos (n) ± SE
Published point count (CoralNet-assisted)15.9
CoralSCOP edited21.9n = 330
Claude (edited photos)13.8n = 351 · SE 0.7

The two computer-vision methods differ by 8.1 pp (13.8–21.9%) and read within 6.0 pp of the published point count (15.9%); the headline is the published point count because it is the site's published value (CoralNet-assisted: most frames were annotated by CoralNet's AI, trained and checked by the author).

Dive history

Coral bleached: computer-vision (CoralNet) estimate from the survey images, per dive, as published in Mayfield (2025, Environments 12:248), Supplementary File S1.

DateTime inMax depth (m)Bottom time (min)Coral bleached (%)
2024-08-31———72.8
2024-09-1410:1232.45470.8
2024-09-1412:2930.359—

Independent surveys nearby

Data availability near this site
Agency / programYear(s)Stations / distanceLink
Aeby et al. (2021)20151 station, 0.36 kmRecords ↓
Furby et al. (2013)20101 station, 0.36 kmRecords ↓
Monroe et al. (2018)20151 station, 0.36 kmRecords ↓
Hard coral cover over time — this site and every independent station within 5 km. Programs are shown separately because they use different methods at different stations; the lines are not one comparable series.
0%15%30%45%60%201020172024Furby et al. (2013) 2010: 23%Monroe et al. (2018) 2015: 37%Aeby et al. (2021) 2015: 60%Coral Reef Diagnostics 2024: 16%Year-averaged across all programs: illustrative only; the programs differ in stations and method, so no trend is claimed (3 years)
Furby et al. (2013) Monroe et al. (2018) Aeby et al. (2021) Coral Reef DiagnosticsYear-average (illustrative only, programs differ)

Within 5 km, 3 independent survey stations recorded hard coral cover in 5 records between 2010 and 2015. The most recent nearby survey is from 2015, so these values predate recent heat stress. This site's own estimate (16%) sits 7 points below the range of these station-year means (23–60%); the methods differ, so the comparison is context, not a like-for-like test.

Collected by other programs using different methods, so these are context for the figures above, not a like-for-like comparison. Where a station was surveyed more than once, the cell shows either the range of its values or, as a single value, the mean of surveys made in one year. Station names are not dive-site names.

Independent survey data near this site
AgencySite / locationDateHard coral cover (%)DistanceLink
Furby et al. (2013)Midshelf reef 2201023% (3 records)0.36 kmdoi:10.1007/s00338-012-0998-5
Monroe et al. (2018)Midshelf reef 2201537%0.36 kmdoi:10.1371/journal.pone.0195814
Aeby et al. (2021)Qita al Kirsh201560%0.36 kmdoi:10.1371/journal.pone.0246854

Data & links

All images from Coral Reef Diagnostics. Data are from Coral Reef Diagnostics and the organizations named in the data sources above.

© Coral Reef Diagnostics.

References

  1. Mayfield AB (2025). Using Tourist Diver Photos to Assess the Effects of Marine Heatwaves on Central Red Sea Coral Reefs. Environments 12:248. PDF
  2. Furby KA, Bouwmeester J, Berumen ML (2013). Susceptibility of central Red Sea corals during a major bleaching event. Coral Reefs 32:505-513. DOI
  3. Monroe AA, Ziegler M, Roik A, Röthig T, Hardenstine RS, Emms MA, et al. (2018). In situ observations of coral bleaching in the central Saudi Arabian Red Sea during the 2015/2016 global coral bleaching event. PLOS ONE 13:e0195814. PDF
  4. Aeby GS, Shore A, Jensen T, Ziegler M, Work T, Voolstra CR (2021). A comparative baseline of coral disease in three regions along the Saudi Arabian coast of the central Red Sea. PLOS ONE 16:e0246854. PDF