Coral Reef Diagnostics

St. Eustatius - STENAPA Reef

Reef Check Foundation
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05
Photo: Anderson Mayfield/Coral Reef Diagnostics
Survey date(s)
2026-02-24
Coordinates
17.4842, -62.9972
Coral cover
4.6%
Claude computer vision (103 photos) · other methods below · median 0.0%
Observations
artificial structurepossible disease
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 — Leeward Caribbean Islands 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 infoLeeward Caribbean Islands (NOAA CRW virtual station)
Photographs
121
49 shown on this page
Site summary
Read this summary in:

A purpose-built artificial reef in St. Eustatius National Marine Park: concrete rings, arches, slabs, and steel hoops laid across a volcanic sand plain, now covered mainly by sponges, with small young coral colonies settling on the structures. Grunts and squirrelfish pack the concrete framework; introduced lionfish and orange cup coral are also on record. Wreck and artificial-structure site: this cover value counts coral growing on man-made structure (steel, concrete, wreck debris) and the bottom around it, so it isn't comparable with natural-reef cover, although it is counted in the St. Eustatius regional mean, which pools three artificial structures and one natural reef.

Max. depth dived
21.9 m
dive-log maximum
Water temp. during survey
26.5°C
-1.6°C vs the 12 months to 2026-08 mean sea temperature (28.1°C)

Eight independent survey stations 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.

These are unedited originals; edited versions will replace them.

18 of the 49 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

STENAPA Reef, St. Eustatius National Marine Park, dived 24 February 2026 — the first dive of the day. This is a purpose-built artificial reef, not a natural one, and the photographs make that unmistakable: the whole dive works a scatter of engineered objects set down on an open sand plain. Conditions were hazy with visible suspended particulate; several wide frames are blue-cast and low-contrast, which limits color-based condition scoring (e.g., Image 9).

Visibility was poor to moderate; wide shots go milky within 10-15 m while close work stays sharp.

General benthic features

Frames show large steel hoops and rebar rings lying flat on the sand, cast concrete blocks with arched window-like openings standing in a line, right-angled concrete beam-and-slab frameworks, and flat plates with drilled circular ports (e.g., Image 7, Image 21, Image 36).

Sponges, not corals, are the dominant cover on the structures (e.g., Image 16).

Yellow and orange tube sponges (Aplysina-type), branching lime-green rope sponges, maroon and scarlet encrusting sheets, pale green encrusting patches, and a pink-brown vase sponge cover most of the hard surface, with pink crustose coralline algae, filamentous turf, and small purple gorgonian sprigs filling the gaps (e.g., Image 29, Image 30, Image 34).

Stony coral is present but sparse and small-colonied: a cluster of knobby mustard-brown Porites-type colonies with pale pink margins, a single clean circular meandroid brain coral (Pseudodiploria/Diploria-type) about a hand-span across, a small yellow-green ridged coral resting on open sand beside a rope sponge, scattered mustard Porites astreoides-type domes on the flat plates, and a few small recruits dotting the concrete (e.g., Image 26, Image 40, Image 42, Image 46, Image 47).

Between the built objects the bottom is fine gray-green volcanic sand, and one stretch of the dive crosses a dense seagrass meadow where dark-bodied fish with trailing dorsal filaments, consistent with French angelfish, drift over the blades — too dim to confirm the identification (e.g., Image 33).

Stony corals are small, isolated heads rather than builders (e.g., Image 11).

Four blurred macros show a cream-pale colony with fully extended polyps — too out of focus to call bleaching either way.

Coral cover

Stressors

The photo review resolved no clearly bleached coral tissue, and the few colonies present look normally pigmented; a computer-vision point count called 3.4% of coral points bleached (2 of 103 photos), but one of those two frames shows a marginal tissue-loss band (possible disease) rather than bleaching: a cream-white band around the whole margin of one colony, edged by a thin yellow rim (photo not shown). The other is a pale massive colony in blue-cast light that cannot be confirmed as bleaching. Two introduced species are on record here: lionfish and orange cup coral Tubastraea coccinea (e.g., Image 8).

Fish and other fauna

Fish use the structure heavily (e.g., Image 3).

One frame holds a dense mixed aggregation of grunts and squirrelfish packed into the concrete framework; another shows yellow-lined goatfish and snapper working the sand alongside the structure line (e.g., Image 18).

A long-spined sea urchin (Diadema antillarum) is tucked into a crevice, spines intact.

Comparisons with other data

Hoeksema et al. (2022) surveyed this site (STENAPA), 0.02 km from the pin. Within 5 km, eight independent stations (Reef Check and XL Catlin Seaview Survey) recorded station-year means of 0.7–38% hard coral cover between 2005 and 2013; the nearest of these, XL Catlin Seaview Survey at transect 25015, 1.63 km away, read 2.0% in 2013.

Other notes

A historic glass bottle lies on the sand.

CV model comparison

Mean 4.6%, median 0.0% across 103 photos.
More infoA few colony-focused photos raise the mean; the median is the typical photo. No computer-vision method yet estimates coral cover accurately on new images, so treat this as indicative rather than a measurement; it is revised as the methods improve.
Headline: Claude computer vision — a blind point count of this site's own photographs.
More infoDINOv3 and CoralSCOP were run on the same photos and are listed for comparison. No diver transect exists for this trip, so agreement between the rows is not accuracy, and no computer-vision method yet estimates coral cover accurately on new images; treat every row as indicative.
MethodHard coral cover (%)Photos (n) ± SE
In-house DINOv318.0n = 103 · SE 0.9
CoralSCOP unedited20.3n = 103 · SE 1.4
Claude4.6n = 103 · SE 0.7

The two computer-vision methods agree within 2.3 pp (18.0–20.3%) and read 13.4–15.7 pp above Claude's blind point count (4.6%); the headline is Claude's blind point count because no transect or manual count exists here.

Independent surveys nearby

Data availability near this site
Agency / programYear(s)Stations / distanceLink
Reef Check2005–20105 stations, 2.04–3.75 kmRecords ↓
XL Catlin Seaview Survey20133 stations, 1.63–4.67 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%10%20%30%40%200520152026Reef Check 2005: 24%Reef Check 2005: 25%Reef Check 2005: 28%Reef Check 2005: 29%Reef Check 2007: 11%Reef Check 2007: 24%Reef Check 2007: 33%Reef Check 2007: 38%Reef Check 2008: 11%Reef Check 2008: 16%Reef Check 2009: 9.4%Reef Check 2009: 16%Reef Check 2009: 22%Reef Check 2010: 26%XL Catlin Seaview Survey 2013: 0.7%XL Catlin Seaview Survey 2013: 2.0%XL Catlin Seaview Survey 2013: 4.4%Coral Reef Diagnostics 2026: 4.6%Year-averaged across all programs: illustrative only; the programs differ in stations and method, so no trend is claimed (7 years)
Reef Check XL Catlin Seaview Survey Coral Reef DiagnosticsYear-average (illustrative only, programs differ)

Within 5 km, 8 independent survey stations recorded hard coral cover in 18 surveys between 2005 and 2013. Of the 4 stations surveyed in more than one year, 3 declined (by 1.0–20 points) and 1 increased (by 14 points) between their first and latest surveys. The longest record, Barracuda Reef Line 1 (Reef Check, 2.04 km away), went from 28% in 2005 to 26% in 2010 (mean of 2 surveys). The most recent nearby survey is from 2013, so these values predate recent heat stress. This site's own estimate (4.6%) sits 2.6 points above the range of these station-year means up to 2 km away (0.7–2.0%), inside the 7-point method-noise floor (inconclusive); 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.

Independent survey data near this site
AgencySite / locationDateHard coral cover (%)DistanceLink
Reef CheckBarracuda Reef Line 12005–201011–28% (range of yearly means; 6 surveys)2.04 km—
Reef CheckBarracuda Reef Line 22005–200724–25% (2 surveys)2.04 km—
Reef CheckMushroom Garden Line 12005–20099.4–33% (4 surveys)3.17 km—
Reef CheckMushroom Garden Line 22005–200724–38% (2 surveys)3.17 km—
Reef CheckTwin Sisters200916%3.75 km—
XL Catlin Seaview Surveytransect 2501520132.0%1.63 kmdoi:10.14264/uql.2019.930
XL Catlin Seaview Surveytransect 2501620130.7%1.66 kmdoi:10.14264/uql.2019.930
XL Catlin Seaview Surveytransect 2501720134.4%4.67 kmdoi:10.14264/uql.2019.930

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. Hoeksema BW, van der Loos LM, van Moorsel GWNM (2022). Coral diversity matches marine park zonation but not economic value of coral reef sites at St. Eustatius, eastern Caribbean. Journal of Environmental Management 320:115829. DOI
  2. Gonzalez-Rivero M, et al. (2019). Seaview Survey photo-quadrat and image classification dataset. The University of Queensland (UQ eSpace) data collection. DOI