Coral Reef Diagnostics

Maldives - Stage

Reef Check Foundation
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05
Photo: Anderson Mayfield/Coral Reef Diagnostics
Country
Survey date(s)
2016-01-17
April 2016 (transect survey)
July 2016 (transect survey)
Coordinates
4.0001, 73.4959
Coral cover
28%
Diver transect survey, July 2016 (Anderson's HARP / Coral Reef CPR long-term monitoring PIT transects; n=20 transects) · details below · median 29%
↘ 56%, 2016-04 → 2016-07
Cover declined by 37 points, from 65% in April 2016 to 28% in July 2016 (same program; 8 and 20 transects, not the same set).
Observations
Heat stress
Most recent heat load record
26 Oct 2026 · Bleaching Watch
5-year thermal stress load
5-year mean max. degree heating weeks (DHW)
2021–2025
NOAA Coral Reef Watch — Maldives 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 infoMaldives (NOAA CRW virtual station)
Photographs
221
35 shown on this page
Site summary
Read this summary in:

Stage is a windward Maldivian fore reef with a shallow, gently sloping top of pale pavement and sand dotted every meter or so with sturdy cauliflower, staghorn, and honeycomb-type colonies, including one almost fluorescent-green branching coral. Photographed along research transects in January 2016, the reef was hit hard when the El Niño heatwave peaked that April, with more than nine in ten colonies bleached.

Max. depth dived
7.4 m
sample-sheet maximum
Water temp. during survey
28.4°Cii
-0.9°C vs the 2016 mean sea temperature (29.3°C)
ii HOBO Pro logger reading at the site (Anderson's 2016 samples sheet), 17 January 2016; not a dive-computer reading.

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

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

8 of the 35 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

Stage is a windward reef on the atoll's east side, classed as fore reef on Anderson's 2016 survey sheet, with a shallow, gently sloping top rather than a dramatic wall: a pale pavement of rock, rubble, and sand stretching into the blue, studded every meter or so with sturdy, self-contained coral colonies (e.g., Image 19, Image 25).

General benthic features

Cauliflower-like clumps compatible with Pocillopora share the ground with thick-fingered digitate and bushy staghorn forms compatible with Acropora — including one startling, almost fluorescent-green colony photographed with its polyps extended in broad daylight — plus honeycomb-surfaced mounds compatible with Goniastrea and its faviid kin (e.g., Image 1, Image 3, Image 11, Image 24).

Coral cover

Stressors

In January 2016 these photos were taken along research transect lines with numbered tags and rulers (e.g., Image 17), and Anderson's sample sheet records all 15 colonies sampled that week as healthy.

One of Anderson's habitat frames from that week nonetheless shows a stark-white colony beside pigmented neighbors, recent mortality, cause not stated (e.g., Image 42).

Months later the picture changed utterly: when the same reef was resurveyed in April 2016 at the peak of the El Niño marine heatwave, more than nine of every ten coral colonies here were bleached. No crown-of-thorns starfish (COTS) or other corallivores were evident.

Comparisons with other data

Apart from our own transect survey shown here, we found no other surveys at this site as of 2026. Within 5 km, three independent stations recorded station-year means of 19–76% hard coral cover between 2015 and 2025; the nearest, Reef Check at Gulhi Island Backreef, 0.87 km away, read 19% in 2022.

CV model comparison

Mean 28%, median 29% across 20 transects.
More infoSame site, April 2016 → July 2016: 65% → 28% (Same reef, same survey program: Anderson's HARP / Coral Reef CPR long-term monitoring PIT transects, April 2016 → July 2016).
Headline: Anderson's own July 2016 point-intercept transects (after the 2016 bleaching); April 2016 is the earlier survey.
More infoThe other rows are comparisons and are never averaged.
MethodHard coral cover (%)Photos (n) ± SE
Transect, July 2016 (headline)28.4
Transect, April 2016 (during the bleaching)64.5
In-house DINOv3, January 2016 photos23.0
CoralSCOP edited, January 2016 photos37.8

The two computer-vision methods disagree by 14.8 pp (23.0–37.8%) and read on both sides of the in-water transect (28.4%); 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
Montefalcone et al. (2020)20151 station, 2.72 kmRecords ↓
Montefalcone et al. 20262024–20251 station, 2.95 kmRecords ↓
Reef Check20221 station, 0.87 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%20%40%60%80%201520202025Montefalcone et al. (2020) 2015: 76%Reef Check 2022: 19%Montefalcone et al. 2026 2024: 43%Montefalcone et al. 2026 2025: 39%Coral Reef Diagnostics 2016: 28%Year-averaged across all programs: illustrative only; the programs differ in stations and method, so no trend is claimed (5 years)
Montefalcone et al. (2020) Reef Check Montefalcone et al. 2026 Coral Reef DiagnosticsYear-average (illustrative only, programs differ)

Within 5 km, 3 independent survey stations recorded hard coral cover in 4 records between 2015 and 2025. The one station surveyed in more than one year declined by 4.0 points between its first and latest surveys. The longest record, Kuda Giri Wreck (Montefalcone et al. 2026, 2.95 km away), went from 43% in 2024 to 39% in 2025. Since 2021, station-year means average 34% (range 19–43%; n = 3 station-years from 3 records). This site's own estimate (28%) sits 9 points above the recent value up to 2 km away (19%); the methods differ, so the comparison is context, not a like-for-like test.

Collected by other programs using different methods (Reef Check uses point-intercept transects), 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
Montefalcone et al. (2020)Cocoa Corner201576% best patch2.72 kmdoi:10.3389/fmars.2020.00587
Reef CheckGulhi Island Backreef202219%0.87 km—
Montefalcone et al. 2026Kuda Giri Wreck2024–202539–43% (2 surveys)2.95 kmdoi:10.1007/s00338-026-02850-x

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. Montefalcone M, Morri C, Bianchi CN (2020). Influence of Local Pressures on Maldivian Coral Reef Resilience Following Repeated Bleaching Events, and Recovery Perspectives. Frontiers in Marine Science 7:587. PDF
  2. Montefalcone M, Bianchi CN, Morri C, Ahmed H, Pancrazi I (2026). Outcomes of the fourth global coral bleaching (2023–2024) in the Maldives. Coral Reefs. DOI