Part of the regional summaries: Maldives - Central (Male Atolls / Ari / Vaavu) and Maldives

A reef caught mid-recovery a year after 2016 bleaching: coralline-algae-capped dead framework and lingering crown-of-thorns scars alongside actively recruiting cauliflower corals and surviving dome corals.
2016 ގެ ހިރިގާ ހުދުވުމުން އަހަރަކަށް ފަހު، އަލުން ރަނގަޅުވަމުން ދާ ފަރެކެވެ: coralline algae އިން ނިވާވެފައިވާ މަރުވެފައިވާ ހިރިގާގެ ފްރޭމްވޯކް އާއި، އަދިވެސް ފެންނަ crown-of-thorns ގެ ކާފައިވާ ލަކުނުތަކާއެކު، އާ ކުދިން ހެދެމުންދާ ކޮލީފްލާވަރ ހިރިގާއާއި ސަލާމަތްވެފައިވާ ގުނބަޒުގެ ސިފައިގެ ހިރިގާ ވެސް ހުރެއެވެ.
AI translation of this summary; the English is authoritative. (low confidence)
Six independent survey stations shown with the program’s logo — click one to see how far it is from this site.
Two other CRD dive sites with their own pages within 5 km shown in orange — click a marker to open its page.
12 of the 25 photographs on this page are shown beside the text that discusses them under "Site description" below.
Look closer and knee-high cauliflower-shaped branching corals are recruiting everywhere across the rubble (e.g., Image 8), massive dome corals (e.g., Image 18) soldier on, and the fish never left.
A year after the 2016 bleaching, whole terraces of dead framework here have been shrink-wrapped in pink crustose coralline algae (e.g., Image 1, Image 3) — nature's primer coat — with dead table corals still standing like abandoned furniture (e.g., Image 12) and crown-of-thorns seastars (plus their fresh feeding scars) hiding in the wreckage.
During a crown-of-thorns removal survey in May 2017, divers from Coral Reef CPR and Carpe Diem Maldives removed 93 crown-of-thorns starfish from this reef (Coral Reef CPR 2017). Red cyanobacterial mats sheet some of the dead tables (e.g., Image 21), and cushion stars, Culcita by Anderson's own identification, graze the framework (e.g., Image 2, Image 3).
Dense black schools boil over the slope (e.g., Image 16), a titan-type triggerfish patrols the rubble (e.g., Image 9), morays — including a gape-jawed honeycomb moray — thread the crevices (e.g., Image 23, Image 25), and the macro hunt turns up a banded boxer shrimp (e.g., Image 20), Clark's-type anemonefish in a red-lipped anemone, and a giant clam flashing a blue-violet mantle.
Montefalcone et al. (2020) surveyed this site (Farukolhufushi Back Faru) in 1999, 0.04 km from the pin. Cover values from that work are not among the survey records shown on this page. Within 5 km, six independent stations recorded station-year means of 1.8–41% hard coral cover between 2010 and 2019; the nearest of these, Montefalcone et al. (2020) at Hulumale Beyru, 0.62 km away, read 15–41% between 2015 and 2016.
Dived three times across the trip, Back Faru reads like a field report on how a Maldivian reef rebuilds.
| Method | Hard coral cover (%) | Photos (n) ± SE |
|---|---|---|
| In-house DINOv3 | 13.9 | |
| CoralSCOP edited | 14.6 | |
| Claude (edited photos) | 6.4 | n = 74 · SE 1.1 |
The two computer-vision methods agree within 0.7 pp (13.9–14.6%) and read 7.5–8.2 pp above Claude's blind point count (6.4%); the headline is Claude's blind point count because no transect or manual count exists here.
See a more detailed, stand-alone version of this table.
| Agency / program | Year(s) | Stations / distance | Link |
|---|---|---|---|
| Montefalcone et al. (2020) | 2015–2019 | 2 stations, 0.62–2.91 km | Records ↓ |
| Reef Check | 2010–2019 | 3 stations, 1.15–2.54 km | Records ↓ |
| XL Catlin Seaview Survey | 2015–2017 | 1 station, 2.81 km | Records ↓ |
Coral Reef DiagnosticsYear-average (illustrative only, programs differ)Within 5 km, 6 independent survey stations recorded hard coral cover in 12 records between 2010 and 2019. Of the 3 stations surveyed in more than one year, 2 were scored by divers or by people annotating photographs: 2 declined (by 21–26 points) between their first and latest surveys. The other 1 was scored by automated image analysis: declined by 12 points, more than the 7-point method-noise floor. The longest record, Banana Reef (Montefalcone et al. 2020, 2.91 km away), went from 40% in 2015 to 19% in 2019. The most recent nearby survey is from 2019, so these values predate recent heat stress. This site's own estimate (6.4%) sits 8.6 points below the range of these station-year means up to 2 km away (15–41%); 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; the XL Catlin Seaview Survey uses photo-transects with automated image annotation), 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.
| Agency | Site / location | Date | Hard coral cover (%) | Distance | Link |
|---|---|---|---|---|---|
| Reef Check | Banana Reef | 2010 | 33% | 1.15 km | — |
| Reef Check | Banana Reef | 2014 | 16% | 2.54 km | — |
| Montefalcone et al. (2020) | Hulumale Beyru | 2015–2016 | 15–41% (range of yearly means; 2 records) | 0.62 km | doi:10.3389/fmars.2020.00587 |
| XL Catlin Seaview Survey | transect 37001 | 2015–2017 | 1.8–14% (2 surveys) | 2.81 km | doi:10.14264/uql.2019.930 |
| Montefalcone et al. (2020) | Banana Reef | 2015–2019 | 12–40% (range of yearly means; 4 records) | 2.91 km | doi:10.3389/fmars.2020.00587 |
| Reef Check | Kuda Banana Reef | 2019 | 7.2%, mean of 2 surveys (5 m and 10 m) | 2.52 km | — |
All images from Coral Reef Diagnostics. Data are from Coral Reef Diagnostics and the organizations named in the data sources above.
© Coral Reef Diagnostics.