Coral Reef Diagnostics

Saudi Red Sea - Rose Reef (Thuwal)

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05
Coral Reef Diagnostics
Photo: Anderson Mayfield/Coral Reef Diagnostics
Survey date(s)
2023-09-08
2023-11-11
2023-11-17
2024-02-09
2024-09-28
2024-10-04
2024-11-09
2024-11-29
Coordinates
22.3106, 38.8867
Coral cover
14%
Published point count (Mayfield 2025; CoralNet-assisted, 720 photos) · details below
Coral bleached
43%
of coral tissue · Mayfield (2025), Environments 12:248
Observations
bleachingrecent mortality
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
546
22 shown on this page; 720 analyzed
Site summary
Read this summary in:

Rose Reef (720 photographs from six of its eight visits) is a near-vertical wall dropping to 32-36 m with a fine mosaic of encrusting faviids, small pocilloporids, and foliose plates, plus black wire corals off the lip. Its shallow reef flat of tabulate and corymbose Acropora showed unmistakable bleaching in the September and November 2023 photographs — and the paper's bleaching figures here range from 23% to 62% of coral tissue.

Max. depth dived
36 m
deepest of 10 logged dives
Water temp. during survey
25–33°C
range of the logged dives

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

One other CRD dive site with its own page within 5 km shown in orange — click a marker to open its page.

13 of the 22 photographs on this page are shown beside the text that discusses them under "Site description" below.

41012131415161719

Photo credit & attribution

Site description

Setting

A small circular reef whose outer face is a near-vertical wall below about 15 m. Several dives ran to 32–36 m and the frames show why: a near-vertical limestone face plastered with small colonies from the surface down, dropping past a fish-swarmed mid-water zone onto a flat, low-relief rubble and sand floor (e.g., Image 2, Image 8).

General benthic features

Viewed from 35 m, that floor is gray-blue, low, almost entirely coralline-crusted rubble with scattered small massives and nothing upright. The wall itself carries a fine-grained mosaic: encrusting and submassive faviids, small pocilloporids, tan and orange encrusting sheets, foliose plates with clean white growing margins, delicate gray and lilac soft corals with extended polyps, sponges and crustose coralline in pinks and reds, and black wire corals springing off the lip into open water (e.g., Image 5, Image 7, Image 9, Image 11).

The shallows are a different reef — a wave-washed flat with tabulate and corymbose Acropora right under the surface, and it is there, in the September and November 2023 frames, that the bleaching in the published record is unmistakable in the photographs.

Coral cover

Stressors

Anderson's 2024 logs record a second bleaching event here: "despite mean temperatures, bleaching was severe" (28 September 2024), "severe bleaching, albeit less >25 m" (4 October 2024, the dive behind the paper's 62% figure), and "extensive coral mortality due to bleaching" (9 November 2024). On the shallow flat in February 2024, the white patches are a mix of crustose coralline algae and old framework and recent mortality of undetermined cause (photos not shown).

Fish and other fauna

Red soldierfish shelter in its crevices, and dense chromis and fusilier schools work the blue (e.g., Image 3, Image 6).

Anderson's frames also show a large barracuda school (11 November 2023) (e.g., Image 20), giant clams (e.g., Image 18, Image 21), and moray eels (e.g., Image 22, Image 23), and the 29 November 2024 log records a large silvertip or possibly tiger shark.

Comparisons with other data

We found no other surveys at this site as of 2026. Within 5 km, two independent stations recorded station-year means of 28–39% hard coral cover in 2015; the nearest, Monroe et al. (2018) at Offshore reef 1, 4.99 km away, read 28% in 2015.

Dive record

Ten dives on eight dates between September 2023 and November 2024 with Coastline (KAUST): one in September 2023, two on 11 November and one on 17 November 2023, one in February 2024, two on 28 September 2024, and one each on 4 October, 9 November, and 29 November 2024.

Survey summary

Rose Reef: surveyed 6 times, Sep 2023–Oct 2024; bleaching ranged from 23% to 62% of coral tissue across visits (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)14.5
In-house DINOv3too few photos (n=3)
CoralSCOP edited23.9n = 455
Claude (edited photos)13.4n = 438 · SE 0.6

The two computer-vision methods disagree by 10.5 pp (13.4–23.9%) and read on both sides of the published point count (14.5%); 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).

In-house DINOv3: this method was run on 3 of 720 photos, under the 10 needed for a value, so it is not shown and is left out of any mean; every other row rests on its own photo count.

Dive history

DateTime inMax depth (m)Bottom time (min)
2023-09-0812:4515.050
2023-11-1110:4536.050
2023-11-1112:4035.050
2023-11-1710:3036.055
2024-02-0910:3932.441
2024-09-2810:2335.855
2024-09-2812:2931.356
2024-10-0412:0915.654
2024-11-0912:3531.558
2024-11-2912:2424.752

Independent surveys nearby

Data availability near this site
Agency / programYear(s)Stations / distanceLink
Aeby et al. (2021)20151 station, 4.99 kmRecords ↓
Monroe et al. (2018)20151 station, 4.99 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. Coral Reef Diagnostics points are survey-year means of CoralNet point annotation from Mayfield (2025, Environments 12:248), Supplementary File S1 (2023: 8 September, 11 November, and 17 November, 364 photos; 2024: 9 February, 28 September, and 4 October, 356 photos). Their mean over all 720 photos is the pooled cover figure on this page.
0%10%20%30%40%201520192024Monroe et al. (2018) 2015: 28%Aeby et al. (2021) 2015: 39%Coral Reef Diagnostics survey 2023: 15%Coral Reef Diagnostics survey 2024: 14%Year-averaged across all programs: illustrative only; the programs differ in stations and method, so no trend is claimed (3 years)
Monroe et al. (2018) Aeby et al. (2021) Coral Reef Diagnostics surveyYear-average (illustrative only, programs differ)

Within 5 km, 2 independent survey stations recorded hard coral cover in 2015. The most recent nearby survey is from 2015, so these values predate recent heat stress. This site's own pooled estimate (14%) is not compared with these surveys: none lies within 2 km.

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
Monroe et al. (2018)Offshore reef 1201528%4.99 kmdoi:10.1371/journal.pone.0195814
Aeby et al. (2021)Shi'b Nazar201539%4.99 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. 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
  2. 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
  3. Mayfield AB (2025). Using Tourist Diver Photos to Assess the Effects of Marine Heatwaves on Central Red Sea Coral Reefs. Environments 12:248. PDF