Coral Reef Diagnostics

Chagos Archipelago - Egmont (BIEG06)

Khaled bin Sultan Living Oceans Foundation — Global Reef Expedition
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05
Photo: Anderson Mayfield/Coral Reef Diagnostics
Survey date(s)
2015-03-11
Coordinates
-6.6394, 71.3395
Coral cover
49%
± 5.4% SE, n = 14 transects · Benthic surveys
Coral bleached
10%
Observations
Heat stress
Most recent heat load record
26 Oct 2026 · Bleaching Warning
5-year thermal stress load
5-year mean max. degree heating weeks (DHW)
2021–2025
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 infoChagos Archipelago, UK (NOAA CRW virtual station)
Photographs
34
Site summary

BIEG06, at Egmont, shows coral stress in three forms — pale, washed-out Acropora plains, colonies with bone-white branch tips, and standing dead branching framework colonized by algae — alongside new coral recruits settling on that dead substrate. Fish life here includes large trevally and snapper schools, plus a chromodorid nudibranch. Surveyed on the Living Oceans Foundation's Global Reef Expedition.

Max. depth dived
18.9 m
sample-sheet maximum
Water temp. during survey
29.4°Cii
CTD-cast midpoint of 29.2–29.6°C
+0.6°C vs the 2015 mean sea temperature (28.8°C)
ii Station CTD-cast midpoint, not a dive reading: midpoint of the station's maximum and minimum CTD water temperature (Living Oceans Foundation Chagos station records); range 29.2–29.6°C.
Bottom time
59 min
in at 10:26

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.

28 of the 34 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

Visibility is fair to hazy and several frames (e.g., Image 3, Image 12, Image 17, Image 19, Image 26, Image 27, Image 34) are soft or backscattered.

General benthic features

Quadrat apparatus is visible in one frame; no scale bar appears anywhere.

This is a branching-Acropora reef, and the frames say so unambiguously. Many of the wide frames look out over near-continuous plains of fine-branched staghorn, digitate, and corymbose Acropora running away from the camera to the limit of visibility. Some frames show dense gold-brown thickets with almost no bare substrate, while Image 2 and Image 33 show the same kind of thicket broken by white sand channels, loose dead branch rubble, and pale pavement. Image 7 adds mixed brown and mauve branching colonies with mustard encrusting sheets over a sandy floor.

Acropora was the most common coral genus on this station's transects (39% of the benthos), followed by Goniopora (4.0%), Goniastrea (2.4%), Favia (1.6%), Psammocora (0.5%), and Lobophyllia, Montipora, and Pavona (0.4% each); turf (15%) was the largest single living non-coral group (all algae together 37%), and bare substrate covered 13% (LOF transects). Among the algal classes, turf led (15% of the benthos), followed by sediment-laden turf (11%) and crustose coralline algae (7.3%).

Coral cover

Stressors

The stress signal here is the site's most important photographic content, and it takes three distinct forms which should not be pooled. First, widespread paling: Image 6 and Image 17 show entire Acropora plains in a washed-out gray-white rather than the golden brown of a healthy stand, and Image 32 shows the same over a broad area beneath an emperor school — they contrast with the gold-brown thickets in other frames, though the paled frames are hazy enough that light and water-column effects cannot be fully separated from tissue paling.

Second, partial-colony bleaching on individual colonies: Image 5 is a clean macro of a Pocillopora with numerous bone-white branch tips against pigmented bases, another frame shows a branching Acropora with extensively whitened tips, and Image 11 records a small cream-white colony that appears wholly bleached.

Third — and most striking — standing dead framework: Image 4 shows a large expanse of intact branching coral skeleton, gray-brown and algal-fuzzed with no live tissue, still standing in growth position among live colonies, with two butterflyfish working over it, and Image 33 shows piles of dead branch rubble across open pavement.

Set against this, three frames (e.g., Image 8, Image 20, Image 24) document the opposite process — small pale Acropora recruits settled directly on dead, CCA-crusted substrate, including one ring of recruits surrounding an algal-covered dead mass.

A single dive therefore records mortality and recruitment on the same reef. Anderson's sampling sheet records 0% bleaching for all six colonies sampled here; one was small and pale, and part of another had died (see Dive record below). The Living Oceans Foundation transects here recorded 0.5% cyanobacteria and 0.1% recently dead coral.

Fish and other fauna

The fish community is dominated by large-bodied predators and grazers. Trevally schools fill four consecutive frames (Image 9, Image 16, Image 29, and Image 36) — sometimes thirty or more animals in one shot, hanging directly over the staghorn; a looser aggregation appears in Image 12, which also carries schooling pinkish-silver emperors or breams.

Snappers appear repeatedly and at close range in Image 3, Image 13, Image 19, Image 26, Image 27, and Image 28, and emperors or breams school over the coral in Image 32 and Image 38.

A gray reef shark appears in Image 2, and a reef shark passes beneath a diver in another frame. Blue-green chromis cloud the staghorn thickets in Image 18 and Image 37, and butterflyfishes work the dead framework in Image 4.



Among the dive's macro subjects is Image 23 — a large chromodorid nudibranch, white to lilac with orange-yellow spots, a purple mantle margin and gill plume raised, not callable to genus or species from a photograph.

Comparisons with other data

Apart from the Living Oceans Foundation survey shown here, we found no other surveys at this site as of 2026. Within 5 km, one independent station, Sheppard et al. (2008) at Egmont, 2.15 km away, read a mean of 19% in 2006.

Dive record

Anderson sampled six colonies on this dive (the sampling sheet). Four are Pocillopora acuta, confirmed by RFLP: CHPd1 (collected 10:38 at 18.5 m; small and pale, living in isolation in the sand under a high sediment load), CHPd2 (10:50, 18.5 m; small, part of the colony dead, the rest apparently healthy), CHPd3 (11:12, 9.4 m; small and healthy, only 2–3 years old), and CHPd4 (11:24, 5.7 m; a small, healthy colony in a shallow, high-light setting). Two are Seriatopora by field call: S. hystrix ChSe1 (10:30, 18.3 m; a large, healthy colony with very thin branches) and Seriatopora sp. ChSe2 (10:44, 18.7 m; tiny, with thin, short branches, a morphology Anderson had not seen before). The dive notes describe an incredibly calm, slightly murky lagoonal back reef with jack schools; P. verrucosa and P. meandrina were present, but Anderson focused on P. acuta and Seriatopora. Pocillopora acuta colonies from this archipelago were analyzed in Thomas et al. (2026, Global Ecology and Biogeography 35:e70305, https://doi.org/10.1111/geb.70305).

Other notes

Thirty-four habitat frames exist for BIEG06 (33 in Anderson's dive folder and one in the "Best of Chagos" folder); close-ups of the colonies sampled are on file but are not shown here. Image 13 is the clearest methodology frame at this site — a diver carrying the white PVC quadrat frame, with a large snapper crossing directly in front of the lens as the frame is carried. Another frame also records the survey in progress, but what the diver there is carrying is a camera rig with twin strobes, not the quadrat.

CV model comparison

Headline is the transect value; every other row is listed beside it for comparison and none is averaged in. ⚠ The reference here is NOT the same instrument as at Mauritius, Oman, Kenya, or the Red Sea.
More infoThose are point counts on the photographs; this is a diver swimming a transect. The models and the reference never saw the same thing. ⚠ SITE-LEVEL ONLY. None of the Chagos photographs (2,500 frames across all stations) can be matched to a transect taken within 200 m, so transect-vs-image comparisons use site means, never individual frames. The transect value is the mean of all of this station's own transects in the expedition's per-transect benthic data. The transect is THE coral-cover value for this site and stands alone. The rows below it are a methods comparison only: no computer-vision value is averaged with it, feeds the headline, or carries over to the site's cover figure.
MethodHard coral cover (%)Photos (n) ± SE
Transect mean (all transects)49.2
CoralNet44.2n = 30 · SE 3.5
In-house DINOv334.0n = 30 · SE 3.6
CoralSCOP edited22.6n = 30 · SE 3.1
Claude31.6n = 30 · SE 4.4

The four computer-vision methods disagree by 21.6 pp (22.6–44.2%) and read 5.0–26.6 pp below the in-water transect (49.2%); the headline is the in-water transect because a diver transect is independent of the photographs.

Independent surveys nearby

Data availability near this site
Agency / programYear(s)Stations / distanceLink
Sheppard et al. (2008)20061 station, 2.15 kmRecords ↓
Spalding et al. (2025)—8 stations, 1.16–3.64 kmRecords ↓

Within 5 km, 1 independent survey station recorded hard coral cover in 2006. The most recent nearby survey is from 2006, so these values predate recent heat stress. This site's own estimate (49%) is not compared with these surveys: none lies within 2 km. 8 further rows in the table have no survey date, so they are listed but not part of this summary.

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. Values above 70% are marked “best patch”: surveys often target the densest coral on a reef, so these may overstate the site as a whole.

Independent survey data near this site
AgencySite / locationDateHard coral cover (%)DistanceLink
Sheppard et al. (2008)Egmont200619% (4 records)2.15 kmdoi:10.3354/meps07436
Spalding et al. (2025)Egmont, NW Lagoon (lagoon, S aspect, 2-3 m)pre-bleaching baseline70%1.16 km—
Spalding et al. (2025)Egmont Outer reef North (ocean, N aspect, 5-8 m)pre-bleaching baseline80% best patch1.46 km—
Spalding et al. (2025)Egmont Outer reef North (ocean, N aspect, 8-10 m)pre-bleaching baseline80% best patch1.46 km—
Spalding et al. (2025)Egmont West (ocean, W aspect, 7-10 m)pre-bleaching baseline30%3.50 km—
Spalding et al. (2025)Egmont West (ocean, W aspect, 12-15 m)pre-bleaching baseline20%3.50 km—
Spalding et al. (2025)Egmont Manta Alley (ocean, NE aspect, 2-5 m)pre-bleaching baseline5.0%3.64 km—
Spalding et al. (2025)Egmont Manta Alley (ocean, NE aspect, 5-8 m)pre-bleaching baseline80% best patch3.64 km—
Spalding et al. (2025)Egmont Manta Alley (ocean, NE aspect, 8-10 m)pre-bleaching baseline80% best patch3.64 km—

Data & links

All images from Coral Reef Diagnostics. Data are from the Khaled bin Sultan Living Oceans Foundation Global Reef Expedition, Coral Reef Diagnostics, and the organizations named in the data sources above.

© Coral Reef Diagnostics.

References

  1. Mayfield AB, Dempsey AC (2026). Using tourist diver images to estimate coral cover and bleaching prevalence in a remote Indian Ocean coral reef system. Oceans 7(1):1. PDF
  2. Sheppard C, Harris A, Sheppard A (2008). Archipelago-wide coral recovery patterns since 1998 in the Chagos Archipelago, central Indian Ocean. Marine Ecology Progress Series 362:109-117. PDF
  3. Spalding M, Bourasseau M, et al. (2025). Coral bleaching and mortality in the Chagos Archipelago, 2024. British Indian Ocean Territory Administration report (gray literature). PDF