Coral Reef Diagnostics

Red Sea

NOAA Coral Reef Watch

Overview of 35 dive sites (33 with their own page). Figures are averages across the sites that report them (n = sites with a value); each site's own page has its individual values. Regional summaries: Saudi Arabia, Egypt.

⬇ Download this overview as a report card
05
Coral Reef Diagnostics
Photo: Anderson Mayfield/Coral Reef Diagnostics — Saudi Red Sea - Um Mankout (Yanbu)
Sites
35
each linked below
Hard coral cover (overview mean)
20% ± 4.8% (std. dev.)
n = 33 of 35 sites. range 13–30%
Water temp. during surveys (overview mean)
31.0°C
n = 33 of 35 sites; surveyed Sep 2023–Nov 2024; 5 sites logged as a range, counted at their midpoint
Coral Health Index (overview mean)
1.95 / 5
n = 5 of 35 sites; scale of zero to five, higher is healthier
Coral bleached (overview mean)
42%
Most recent water temperature record
26 Oct 2026 · Al Madinah and Makkah
Most recent heat stress record
26 Oct 2026 · Alert Level 2
Mean annual max degree heating weeks (DHW), last 5 years
2021–2025 · regional mean of 35 sites, 2 stations
Highest annual heat stress
in 2024 · Egypt
Severe heat-stress years
1985–2025 · 7 in the last 10 years
Heat-stress figures: NOAA Coral Reef Watch 5-km virtual stations: Al Madinah and Makkah; Egypt. Each pill links its source record and carries the values behind it.

Heat stress

0481216202428Week of 2023-07-09: DHW 1.0°C-weeks (below the bleaching alert threshold); SST 29.92°CWeek of 2023-07-16: DHW 2.9°C-weeks (below the bleaching alert threshold); SST 30.55°CWeek of 2023-07-23: DHW 5.3°C-weeks (Alert Level 1: significant bleaching likely); SST 31.37°CWeek of 2023-07-30: DHW 7.6°C-weeks (Alert Level 1: significant bleaching likely); SST 31.76°CWeek of 2023-08-06: DHW 10.0°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.67°CWeek of 2023-08-13: DHW 12.1°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.44°CWeek of 2023-08-20: DHW 13.9°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 32.30°CWeek of 2023-08-27: DHW 15.5°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 32.08°CWeek of 2023-09-03: DHW 17.1°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 32.09°CWeek of 2023-09-10: DHW 18.3°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.96°CWeek of 2023-09-17: DHW 19.2°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.16°CWeek of 2023-09-24: DHW 19.2°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.85°CWeek of 2023-10-01: DHW 19.2°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.89°CWeek of 2023-10-08: DHW 17.9°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.49°CWeek of 2023-10-15: DHW 16.0°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.41°CWeek of 2023-10-22: DHW 13.6°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.88°CWeek of 2023-10-29: DHW 11.2°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.72°CWeek of 2023-11-05: DHW 8.9°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.89°CWeek of 2023-11-12: DHW 6.8°C-weeks (Alert Level 1: significant bleaching likely); SST 30.24°CWeek of 2023-11-19: DHW 5.1°C-weeks (Alert Level 1: significant bleaching likely); SST 29.24°CWeek of 2023-11-26: DHW 3.4°C-weeks (below the bleaching alert threshold); SST 29.13°CWeek of 2023-12-03: DHW 1.9°C-weeks (below the bleaching alert threshold); SST 28.80°CWeek of 2023-12-10: DHW 0.7°C-weeks (below the bleaching alert threshold); SST 28.68°CWeek of 2024-06-30: DHW 0.8°C-weeks (below the bleaching alert threshold); SST 30.81°CWeek of 2024-07-07: DHW 2.5°C-weeks (below the bleaching alert threshold); SST 31.10°CWeek of 2024-07-14: DHW 4.7°C-weeks (Alert Level 1: significant bleaching likely); SST 31.09°CWeek of 2024-07-21: DHW 7.5°C-weeks (Alert Level 1: significant bleaching likely); SST 31.78°CWeek of 2024-07-28: DHW 10.6°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 32.21°CWeek of 2024-08-04: DHW 13.6°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 32.69°CWeek of 2024-08-11: DHW 16.2°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.44°CWeek of 2024-08-18: DHW 18.6°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.40°CWeek of 2024-08-25: DHW 20.7°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.55°CWeek of 2024-09-01: DHW 22.4°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.61°CWeek of 2024-09-08: DHW 24.3°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.36°CWeek of 2024-09-15: DHW 25.7°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.86°CWeek of 2024-09-22: DHW 26.2°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.31°CWeek of 2024-09-29: DHW 25.4°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.98°CWeek of 2024-10-06: DHW 23.5°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.38°CWeek of 2024-10-13: DHW 21.2°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.74°CWeek of 2024-10-20: DHW 18.4°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.30°CWeek of 2024-10-27: DHW 15.3°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.90°CWeek of 2024-11-03: DHW 12.3°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.54°CWeek of 2024-11-10: DHW 9.7°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 28.83°CWeek of 2024-11-17: DHW 7.4°C-weeks (Alert Level 1: significant bleaching likely); SST 28.74°CWeek of 2024-11-24: DHW 5.4°C-weeks (Alert Level 1: significant bleaching likely); SST 28.13°CWeek of 2024-12-01: DHW 3.7°C-weeks (below the bleaching alert threshold); SST 27.52°CWeek of 2024-12-08: DHW 1.8°C-weeks (below the bleaching alert threshold); SST 27.39°CWeek of 2024-12-15: DHW 0.5°C-weeks (below the bleaching alert threshold); SST 26.57°CWeek of 2025-07-06: DHW 0.3°C-weeks (below the bleaching alert threshold); SST 30.58°CWeek of 2025-07-13: DHW 1.8°C-weeks (below the bleaching alert threshold); SST 31.00°CWeek of 2025-07-20: DHW 3.6°C-weeks (below the bleaching alert threshold); SST 31.56°CWeek of 2025-07-27: DHW 6.1°C-weeks (Alert Level 1: significant bleaching likely); SST 31.82°CWeek of 2025-08-03: DHW 8.5°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.57°CWeek of 2025-08-10: DHW 10.5°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.76°CWeek of 2025-08-17: DHW 12.3°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.59°CWeek of 2025-08-24: DHW 13.9°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.44°CWeek of 2025-08-31: DHW 15.3°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.99°CWeek of 2025-09-07: DHW 16.3°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.61°CWeek of 2025-09-14: DHW 16.6°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.97°CWeek of 2025-09-21: DHW 16.6°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.92°CWeek of 2025-09-28: DHW 16.6°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.14°CWeek of 2025-10-05: DHW 16.1°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.48°CWeek of 2025-10-12: DHW 14.6°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 28.53°CWeek of 2025-10-19: DHW 12.6°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.74°CWeek of 2025-10-26: DHW 10.1°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.41°CWeek of 2025-11-02: DHW 7.9°C-weeks (Alert Level 1: significant bleaching likely); SST 28.68°CWeek of 2025-11-09: DHW 5.8°C-weeks (Alert Level 1: significant bleaching likely); SST 29.43°CWeek of 2025-11-16: DHW 4.1°C-weeks (Alert Level 1: significant bleaching likely); SST 27.67°CWeek of 2025-11-23: DHW 2.5°C-weeks (below the bleaching alert threshold); SST 27.67°CWeek of 2025-11-30: DHW 1.1°C-weeks (below the bleaching alert threshold); SST 27.95°CWeek of 2025-12-07: DHW 0.2°C-weeks (below the bleaching alert threshold); SST 27.82°CWeek of 2026-07-19: DHW 0.3°C-weeks (below the bleaching alert threshold); SST 29.92°CWeek of 2026-07-26: DHW 1.3°C-weeks (below the bleaching alert threshold); SST 30.30°CWeek of 2026-08-02: DHW 2.8°C-weeks (below the bleaching alert threshold); SST 30.29°CWeek of 2026-08-09: DHW 4.6°C-weeks (Alert Level 1: significant bleaching likely); SST 30.72°CWeek of 2026-08-16: DHW 6.6°C-weeks (Alert Level 1: significant bleaching likely); SST 30.93°CWeek of 2026-08-23: DHW 8.7°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 31.02°CWeek of 2026-08-30: DHW 10.9°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.76°CWeek of 2026-09-06: DHW 12.4°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.45°CWeek of 2026-09-13: DHW 13.7°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 30.19°CWeek of 2026-09-20: DHW 14.3°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.63°CWeek of 2026-09-27: DHW 14.3°C-weeks (Alert Level 2+: severe bleaching and significant mortality likely); SST 29.47°C22242628303234Bleaching threshold 30.8°C2023202420252026SST (°C)DHW (°C-weeks)
sea surface temperature (SST) (left axis)DHW under 2DHW 2–3DHW 3–5DHW 5–8DHW 8–10DHW over 10 (🔥 above 12)
Daily SST (line) and weekly maximum Degree Heating Weeks (bars), Jan 2023–Oct 2026, NOAA Coral Reef Watch 5-km Egypt virtual station. Dashed line: bleaching threshold (maximum monthly mean 29.8°C + 1°C). DHW ≥ 4: bleaching likely; ≥ 8: severe bleaching and mortality likely. A bar is drawn only where DHW exceeds zero, so a stretch with no bar is accumulated heat stress of zero, not missing data — the SST line runs the full period.

Long-term record: 14 years from 1985 through 2025 reached 8 or more °C-weeks at NOAA’s Egypt, Al Madinah and Makkah stations. Download the annual DHW data (CSV).

35 sites in this region — click a marker to open that site.

Overview

The Red Sea is geologically a young ocean, a basaltic spreading rift that has been pulling Africa and Arabia apart for some 70 million years. Its shallow link to the Indian Ocean has closed many times, most recently during the Pleistocene, and many of today's reefs are thin modern veneers over older Pleistocene reefs (Spalding et al. 2001). Together with the Gulf of Aden it may be the most biologically diverse reef area outside Southeast Asia, with many endemic species. South of the Gulfs of Suez and Aqaba both shores are lined with fringing reefs that run unbroken for tens of kilometers, usually with narrow reef flats. On the Arabian side the continental shelf is narrow or absent in the north and broadens fairly rapidly south of about 20°N; offshore, the Al Wadj Bank holds a complex of fringing, patch, and barrier reefs with small islands, and from Al Wadj to Jeddah runs a broken barrier-type structure that has been called the Little Barrier Reef. Surveys between 1997 and 1999 recorded about 260 hard coral species on the Saudi coast. Spalding et al. (2001) estimate about 6,660 km² of coral reef for Saudi Arabia, a national figure that includes its Arabian Gulf coast, and about 3,800 km² for Egypt; Souter et al. (2021) give 13,605 km² for the Red Sea and Gulf of Aden together and 7,800 km² for the northern and central Red Sea subregion, which is the subregion all but two sites on this page belong to; the two Al Qunfudah reefs sit south of it.

This page gathers 35 sites in two national branches. Saudi Arabia holds 24 in three units: Jeddah / KAUST (Thuwal) / Rabigh with 15 — eight off Thuwal worked with Coastline (KAUST), six off Jeddah, and one shore-entry reef north of Rabigh — Yanbu with seven offshore reefs in the Yanbu and Umluj area dived with Umluj Dive Center, and South of Jeddah with two unnamed reefs off Al Qunfudah, dived together on 30 August 2024 with Al Qunfudah Diver. Egypt holds 11 in one unit, four at Marsa Nakari and seven at Wadi Lahami, dived with Red Sea Diving Safari. Thirty-three fall in one NOAA Coral Reef Watch ecoregion, Northern and Central Red Sea; the two Al Qunfudah reefs fall in Southern Red Sea, so the page spans two heat-stress provinces, with 33 of 35 sites in the northern one. The settings run from a wave-lit reef flat a meter or two under the surface at Alrass Alakhdar and low-relief house-reef pavement, rubble, and sand at Marsa Nakari, through high-relief spur-and-groove honeycombed with swim-throughs at Cement Reef, submerged pinnacles at Habili El Ghadeer, Habili Daisy, and Habili Gazella, and Porites-carpeted slopes at Um Mankout, Om Halhala, and Salah, to near-vertical walls at Rose Reef and Thetis and eroded, heavily bioeroded caverns rising from sand at Cave Reef. Three members are artificial or barely coralline — the Cement Wreck and Chicken Wreck off Thuwal and Jeddah, and Drogon Corals, mostly a sand plain with isolated bommies — while a fourth, Abu Galawa-small, is a steel shipwreck with scattered coral colonies, most on its open ribs. Recorded maximum depths run from 13.4 m at Habili Gazella to 36.0 m on Rose Reef's wall at the 24 sites that have one. Two sites have no photographs and no cover value at all: Middle Reef off Thuwal and Al Shbareer reef off Yanbu.

Published point-count cover exists for 33 of the 35 sites and averaged 20%, a narrow band from 13% on the Cement Wreck to 30% at Alrass Alakhdar. The two branches are close together: 19% across the 22 Saudi sites with a value and 22% across all 11 Egyptian sites. Algal cover stayed low everywhere, from 3.4% at Om Halhala to 12% at Long Reef, with the Egyptian sites clustered at the low end. The community is consistent along both coasts — pocilloporids in lavender, magenta, rose, and hot-pink color forms, corymbose, digitate, staghorn, and table Acropora, knobby and columnar Porites, Seriatopora hystrix, faviids, and Millepora-type fire coral, with cobalt Acropora on the upper slope at Cement Reef. Individual sites stand out for structure rather than for cover. Coral Gardens off Jeddah is built on giant Porites mounds several meters across; Um Mankout carries a near-continuous Porites framework with almost no bare pavement; Anderson's Reef-II is set apart by a bommie the size of a small building with its crown covered in lilac and gold arborescent soft corals; and Shabrour-north is a broad sand plain studded with bommies and low patch reefs.

What this set records is the 2023-24 Red Sea marine heatwaves: 33 of the 35 sites carry a bleaching percentage. Across them, bleaching averaged 42% of coral tissue and ranged from 14% at the first Al Qunfudah reef to 74% at Shabrour-north in Wadi Lahami. The two branches read very differently. The Egyptian mean is 59% and ten of the eleven Egyptian sites are above 50%; the Saudi mean is 33% and only four of the twenty-two Saudi sites with a value are. Shabrour-north reached 74% and Shark Reef off Thuwal 72%, where whole slopes were white and three crown-of-thorns starfish were photographed amid the bleaching. Branching, massive, and fire corals were all affected on the Saudi coast, and branching and massive corals on the Egyptian coast, where the fire coral was dead and overgrown with algae: at Om Halhala the Porites framework bleached en masse while nearby Acropora thickets held color, at Bhadur Reef soft corals, fungiids, and anemones bleached along with the hard corals, and the corals on the Abu Galawa-small wreck were almost entirely white. Some colonies showed fluorescent (colorful) bleaching, among them a pale-blue thicket at Shabrour-south and vivid pink-lavender, blue, and yellow colonies at Shark Reef and north Rabigh. Other pressures were photographed too: a derelict fish trap overgrown by corals and a diver towing a trap full of fish at Um Mankout, where Anderson logged "clear evidence of overfishing"; an old line across Cement Reef and a fouled pipe at Al Fasmah; and red or rust-orange cyanobacterial mats over coral bommies, dead rock, or dead framework at Gazella Reef, Habili Daisy, and Shark Reef.

That country gap should not be read as a difference between Egyptian and Saudi reefs, because it is confounded with when each coast was dived. All eleven Egyptian sites were surveyed in a single four-day window, 20 to 23 September 2024, at about 25.5 to 26.0°C-weeks of accumulated heat, more than at any Saudi visit, with a published dive temperature of 31.5°C at Marsa Nakari-North (Mayfield 2025, Environments 12:248, Appendix A) — a snapshot taken at the peak of a severe event. The 24 Saudi sites were surveyed over fifteen months, September 2023 to November 2024, and several were dived repeatedly in winter and in summer, at per-visit heat loads from 1.4 to 22.3°C-weeks and, on seven visits, none recorded at all; their site pages list each visit. The Saudi visits made at the heaviest heat loads bleached in the Egyptian band: Bhadur Reef 62% at about 22.3°C-weeks, Shark Reef 72% at 20.6 and 21.8, Thetis 62% at 19.9 in October 2023. Accumulated heat does not explain the scatter either, though. The clearest case is Al Qunfudah: its two reefs sat at about 20.4°C-weeks and bleached 14% and 18%. The north Rabigh shore site read 65% at about 16.9°C-weeks while Long Reef read 20% at 16.5; Anderson's Reef-I and Reef-II read 17% and 19% at 11.9; and seven visits bleached with no accumulated heat stress recorded at all: Rose Reef at 23%, Cave Reef at 27%, Abu Ejeiah at 13%, and Cement Reef at 20% in February 2024, and Abu Galawa at 25%, Mr. Umluj at 28%, and the Cement Wreck at 25% in April 2024. Where the heat did bite, cover followed: Thetis went from 33% in October 2023 to 13% in August 2024, when the wall was darker and dominated by soft corals and sponges.

Two independent comparisons sit beside these figures rather than being averaged into them. At Marsa Nakari, Reef Check stations 0.10 and 0.25 km from the two house-reef sites recorded 29% and 27% hard coral in 2025 (40% and 47% in 2024, against CRD's 25% and 23% that year — a different method on what may be the same reef). At Wadi Lahami, Reef Check's House Reef 2 station, 1.55 to 1.85 km from the two Shabrour sites, recorded 56% in 2009 and 44% in 2023, against 24% and 25% in September 2024. These 33 sites are also the reference region for CRD's multi-model computer-vision comparison, in which several segmentation models are being scored against a set of frames hand-annotated by Anderson. Every cover figure on this page is the published CoralNet point count of Mayfield (2025, Environments 12:248), in which most frames were annotated by CoralNet's AI, trained and checked by Anderson. For the longer view, Souter et al. (2021), writing before the 2023-24 heatwaves, had coral cover in the northern and central Red Sea falling from 35% in 1997 to 30% in 2002 and then climbing slowly to 39% by 2019, while algal cover rose from 5.2% in 2010 to 11.5%. They name tourism and coastal development as the main local drivers of loss in the northern Red Sea and land runoff, eutrophication, and overfishing in the central Red Sea, with Saudi Arabia's Vision 2030 coastal tourism plans an added pressure; and they note that the region's only sampling units with more than fifteen years of data lie on the Egyptian coast, where more frequent disturbance has produced a stepwise decline, with half of those that lost at least a fifth of their coral never regaining 90% of it.

Highlights

Notable observations (24)

Coral cover over time (pooled)

One point per year: the mean of every hard coral cover value available for this region that year — Anderson’s own dives and every independent survey station within 5 km of them. The vertical bar is the full range behind that mean. Different programs use different methods at different stations, so this is a regional summary, not a single comparable series. One value above 70% was excluded as a best-patch figure rather than a site mean. Years resting on fewer than three values are drawn as smaller points (2004, 2006, 2011, 2017, 2019, 2022). Non-CRD points are from Reef Check Foundation, Aeby et al. (2021), Khalil et al. (2017), Furby et al. (2013), Monroe et al. (2018), and MERMAID project “Egyptian Red Sea Initiative - Egypt”. Marker shape: Anderson’s own dives, other organizations’ surveys, a mix of both, that year.
0%17%34%51%68%2003201420262003: mean 43% of 3 values (range 39–49%)2004: mean 48% of 1 value2005: mean 42% of 5 values (range 23–61%)2006: mean 29% of 2 values (range 9.4–49%)2007: mean 30% of 4 values (range 11–47%)2009: mean 45% of 3 values (range 30–56%)2010: mean 32% of 4 values (range 23–37%)2011: mean 43% of 2 values (range 39–46%)2012: mean 45% of 5 values (range 30–53%)2013: mean 30% of 9 values (range 14–53%)2014: mean 32% of 5 values (range 4.4–52%)2015: mean 43% of 9 values (range 28–60%)2017: mean 53% of 1 value2018: mean 44% of 4 values (range 37–52%)2019: mean 59% of 1 value2022: mean 53% of 1 value2023: mean 26% of 10 values (range 12–44%)2024: mean 23% of 34 values (range 12–58%)2025: mean 22% of 3 values (range 11–29%)2026: mean 53% of 6 values (range 41–67%)
Sites in this region (35)

% coral cover by method

This page pools more than one published study area; each is tabulated separately below because their reference sets are different.

Saudi Arabia

Pooled across 22 dive sites

MethodMean % coral coverStd. dev. between dive sitesn dive sitesNote
Published point count (CoralNet-assisted)19%±4.822—
CoralSCOP (SAM-based mask-sum), edited photos26%±4.322—
Claude (Anthropic), blind point count19%±7.222—
In-house DINOv3 point classifier38%±1351 of these 5 values rests on 10–19 photographs (*)

The mean is an UNWEIGHTED mean of the dive site values — each dive site counts once, whatever its photo count — which is the convention of the published tables and of every other figure on this page. Each value is the one printed on that dive site's own page; a page that prints no value for a method (fewer than 10 photographs) is left out of that method's mean.

Closest to the reference

Over the dive sites where an independent reference exists, Claude (Anthropic), blind point count sits closest to it — a mean absolute deviation of 2.8 pp across 5 dive sites, then In-house DINOv3 point classifier 16.8 pp (n=5). Not in this ranking: CoralSCOP (edited), which measures coral area rather than points. A mean absolute deviation is not an accuracy score: a model with a consistent offset is correctable, while one with the same deviation scattered in both directions is not.

By dive site

Dive sitePublished point countCoralSCOP (edited)ClaudeDINOv3
Abu Ejeiah (Thuwal)15%
n=417
24%
n=367
17%
n=366
too few photos
n=4
Cement Reef (Thuwal)22%
n=469
29%
n=471
24%
n=478
26%
n=95
Cement Wreck (Thuwal)13%
n=383
21%
n=391
12%
n=387
34%*
n=11
Rose Reef (Thuwal)14%
n=720
24%
n=455
13%
n=438
too few photos
n=3
Long Reef (Thuwal)14%
n=90
24%
n=91
12%
n=88
—
Cave Reef (Thuwal)16%
n=68
22%
n=70
16%
n=65
too few photos
n=2
Shark Reef (Thuwal)16%
n=421
22%
n=330
14%
n=351
—
Drogon Corals (Jeddah)14%
n=67
22%
n=66
10%
n=65
too few photos
n=1
Chicken Wreck (Jeddah)17%
n=251
24%
n=153
10%
n=171
27%
n=126
Anderson's Reef-I (Jeddah)23%
n=146
29%
n=147
20%
n=146
too few photos
n=1
Coral Gardens (Jeddah)28%
n=300
29%
n=254
25%
n=271
44%
n=156
Bhadur Reef (Jeddah)21%
n=222
27%
n=167
18%
n=174
—
Anderson's Reef-II (Jeddah)21%
n=174
25%
n=174
19%
n=175
too few photos
n=3
north Rabigh (shore) (Rabigh)24%
n=173
30%
n=122
23%
n=158
57%
n=175
Um Mankout (Yanbu)26%
n=228
32%
n=229
29%
n=227
too few photos
n=2
Alrass Alakhdar (Yanbu)30%
n=59
36%
n=58
39%
n=57
—
Al Fasmah (Yanbu)22%
n=116
31%
n=116
27%
n=116
—
Thetis (Yanbu)16%
n=170
21%
n=171
12%
n=169
too few photos
n=5
Abu Galawa (Yanbu)18%
n=138
31%
n=138
22%
n=135
—
Mr. Umluj (Yanbu)17%
n=326
22%
n=326
17%
n=326
—
unnamed site 1 (Al Qunfudah)16%
n=130
31%
n=119
18%
n=123
—
unnamed site 2 (Al Qunfudah)17%
n=80
24%
n=70
11%
n=86
—
Thuwal: published area value (Mayfield 2025, Table 4)16%
n=2,567
———
Jeddah: published area value (Mayfield 2025, Table 4)22%
n=1,160
———
Rabigh: published area value (Mayfield 2025, Table 4)24%
n=173
———
Yanbu: published area value (Mayfield 2025, Table 4)20%
n=1,036
———
Qunfudah: published area value (Mayfield 2025, Table 4)17%
n=210
———

n under each value is the number of photographs that method scored at that dive site. ⚠ marks a cell that is not an independent check. * marks a value resting on only 10–19 photographs, which is less certain.

Reference: each dive site's own published CoralNet point count by the author, as its page prints it (CoralNet-assisted, on that site's photographs; Mayfield 2025, Environments 12:248). Denominator: coral points / (30 − water − fish points); unknown points stay in the denominator (Mayfield 2025 convention); diver points are excluded as well, per the Red Sea paper. Source: each member dive-site page. Each row is a member dive site, and every value is the one printed on that dive site's own page; the computer-vision values ran on that site's own photographs. No value here comes from computer vision run on an area's representative photographs. Rows labeled “published area value” are the published area values (Mayfield 2025, Environments 12:248, Table 4); each summarizes the same dives as the dive-site rows beside it, so none is in any mean on this page.

Egypt

Pooled across 11 dive sites

MethodMean % coral coverStd. dev. between dive sitesn dive sitesNote
Published point count (CoralNet-assisted)22%±4.411—
CoralSCOP (SAM-based mask-sum), edited photos28%±3.27—
CoralSCOP (SAM-based mask-sum), unedited photos26%±3.011—
Claude (Anthropic), blind point count22%±4.311—
In-house DINOv3 point classifier46%±0.63—

Closest to the reference

Over the dive sites where an independent reference exists, Claude (Anthropic), blind point count sits closest to it — a mean absolute deviation of 1.7 pp across 3 dive sites, then In-house DINOv3 point classifier 23.7 pp (n=3). Not in this ranking: CoralSCOP (unedited) and CoralSCOP (edited), which measure coral area rather than points.

By dive site

Dive sitePublished point countCoralSCOP (edited)CoralSCOP (unedited)ClaudeDINOv3
Shabrour-north (Wadi Lahami)24%
n=100
30%
n=74
28%
n=108
21%
n=92
45%
n=99
Gazella Reef (Wadi Lahami)17%
n=214
22%
n=208
22%
n=222
18%
n=204
46%
n=30
Shabrour-south (Wadi Lahami)25%
n=223
29%
n=129
27%
n=241
24%
n=221
—
Salah (Wadi Lahami)28%
n=218
—29%
n=231
28%
n=212
—
Abu Galawa-small (Wadi Lahami)21%
n=192
—23%
n=203
26%
n=188
—
Habili Daisy (Wadi Lahami)23%
n=52
too few photos
n=8
24%
n=58
18%
n=50
—
Habili Gazella (Wadi Lahami)18%
n=181
—22%
n=190
19%
n=176
—
Nakari House Reef-South (Marsa Nakari)25%
n=102
28%
n=107
26%
n=119
24%
n=103
46%
n=30
Habili El Ghadeer (Marsa Nakari)13%
n=161
24%
n=148
24%
n=168
16%
n=147
—
Om Halhala (Marsa Nakari)24%
n=216
30%
n=200
30%
n=221
29%
n=206
—
Marsa Nakari-North (Marsa Nakari)23%
n=195
29%
n=188
28%
n=205
23%
n=172
—
Wadi Lahami: published area value (Mayfield 2025, Table 4)22%
n=1,180
————
Marsa Nakari: published area value (Mayfield 2025, Table 4)21%
n=674
————

n under each value is the number of photographs that method scored at that dive site. ⚠ marks a cell that is not an independent check.

Reference and denominator: as above. Source: each member dive-site page.

Nearby external survey stations

116 independent survey records within 5 km of a site in this region (each record counted once; 76 lines, and a line that pools several records says how many).

Show all 116 records

All images from Coral Reef Diagnostics. Data are from Coral Reef Diagnostics, Reef Check Foundation, NOAA Coral Reef Watch, Aeby et al. (2021), Khalil et al. (2017), Furby et al. (2013), and Monroe et al. (2018).

© 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. Spalding MD, Ravilious C, Green EP (2001). World Atlas of Coral Reefs. University of California Press, Berkeley. PDF
  3. Souter D, Planes S, Wicquart J, Logan M, Obura D, Staub F (eds) (2021). Status of Coral Reefs of the World: 2020. International Coral Reef Initiative / Global Coral Reef Monitoring Network. 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
  5. Khalil MT, Bouwmeester J, Berumen ML (2017). Spatial variation in coral reef fish and benthic communities in the central Saudi Arabian Red Sea. PeerJ 5:e3410. DOI
  6. Furby KA, Bouwmeester J, Berumen ML (2013). Susceptibility of central Red Sea corals during a major bleaching event. Coral Reefs 32:505-513. DOI
  7. 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