Coral Reef Diagnostics

Saudi Red Sea - Cement Wreck (Thuwal)

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05
Photo: Anderson Mayfield/Coral Reef Diagnostics
Survey date(s)
2023-09-08
2024-04-27
2024-07-26
2024-11-09
Coordinates
22.3867, 38.8521
Coral cover
13%
Published point count (Mayfield 2025; CoralNet-assisted, 383 photos) · details below
Coral bleached
26%
of coral tissue · Mayfield (2025), Environments 12:248
Observations
shipwreckbleaching
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
416
20 shown on this page
Site summary
Read this summary in:

Cement Wreck pairs a low-cover steel shipwreck — its hull colonized only patchily by coralline algae, sponges, and scattered small corals — with a steeper natural reef slope beside it carrying massive boulder colonies, a large Diploastrea heliopora colony, and tabulate Acropora. Across three visits (Sept 2023, April 2024, July 2024) cover ran 10-17% and 19-32% of coral tissue was bleached, but bleaching did not track heat stress: 25% was bleached in April 2024 with no accumulated heat stress, and 19% during the July 2024 heatwave; a blue-spotted stingray sheltering under the hull was a fauna highlight.

Max. depth dived
18 m
deepest of 2 logged dives
Water temp. during survey
28–33°C
Published dive temperature (Mayfield 2025, Environments 12:248, Appendix A): 33°C on 8 September 2023, 28°C on 27 April 2024, and 32.5°C on 26 July 2024.

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

Three other CRD dive sites with their own pages within 5 km shown in orange — click a marker to open its page.

8 of the 20 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

Setting

A steel shipwreck lying on sand alongside the Thuwal reef line, dived four times between September 2023 and November 2024 with Coastline (KAUST), with a per-visit cover series attached to it. On the fourth dive, on 9 November 2024, Anderson logged that most of the corals on the wreck had died from bleaching.

General benthic features

The wreck itself dominates the dive: a substantial iron hull broken along its length, deck beams and bulkheads standing proud of a pale sand bottom, plating rusted to deep red-brown and colonized in patches rather than uniformly — encrusting coralline algae, small sponges, turf, barnacle scars, and scattered small hard corals rather than the dense soft-coral cladding that older Red Sea wrecks often carry (e.g., Image 1, Image 3, Image 4).

It is a low-cover artificial substrate. The natural reef beside it is a steeper mixed slope: cream and tan massive boulder colonies, a very large Diploastrea heliopora colony (Anderson's identification), tabulate Acropora, encrusting plates, lavender pocilloporids, cream-white soft corals, and encrusting sponges, over pavement, and rubble that carry considerably more coralline algae than live coral (e.g., Image 2, Image 6, Image 7, Image 8, Image 9).

Coral cover

Fish and other fauna

Fauna is wreck-typical: a blue-spotted stingray tucked under a hull plate on the sand, a black-and-white polyclad flatworm on a massive coral nodule; anthias and small reef fish swim over the reef edge.

Comparisons with other data

Apart from our own published survey shown here, we found no other surveys confirmed at this site as of 2026. Within 5 km, one independent station, Furby et al. (2013) at Offshore reef 1, 1.88 km away, read a mean of 31% in 2010.

Survey summary

Cement Wreck: surveyed 3 times, Sep 2023–Jul 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, DINOv3 ran on the site's benchmark frames (the photographs the author annotated point by point), 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)12.8
In-house DINOv333.7*n = 11
CoralSCOP edited21.1n = 391
Claude (edited photos)12.4n = 387 · SE 0.7

The three computer-vision methods disagree by 21.3 pp (12.4–33.7%) and read on both sides of the published point count (12.8%); 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).

*Based on only 11 reef-habitat photos; this estimate is less certain.

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 (%)
2023-09-0810:5514.05032.0
2024-04-27———25.3
2024-07-26———18.7
2024-11-0910:0018.060—

Independent surveys nearby

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. Coral Reef Diagnostics points are survey-year means of CoralNet point annotation from Mayfield (2025, Environments 12:248), Supplementary File S1 (2023: 8 September, 133 photos; 2024: 27 April and 26 July, 250 photos). Their mean over all 383 photos is the pooled cover figure on this page.
0%10%20%30%40%201020172024Furby et al. (2013) 2010: 31%Coral Reef Diagnostics survey 2023: 12%Coral Reef Diagnostics survey 2024: 13%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) Coral Reef Diagnostics surveyYear-average (illustrative only, programs differ)

Within 5 km, 1 independent survey station recorded hard coral cover in 2010. The most recent nearby survey is from 2010, so these values predate recent heat stress. This site's own pooled estimate (13%) sits 18 points below the one nearby survey station (31%); 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)Offshore reef 1201031% (3 records)1.88 kmdoi:10.1007/s00338-012-0998-5

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