Atlantic and Gulf Rapid Reef Assessment
Coral Reef Diagnostics

SVG - Mayreau Gardens (CO2 vent site)

Reef Check Foundation
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05
Photo: Anderson Mayfield/Coral Reef Diagnostics
Survey date(s)
2019-09-26
2019-09-27
2019-09-28
2019-09-29
2019-09-30
2019-10-01
Coordinates
12.6283, -61.3782
Coral cover
23%
Claude computer vision (66 edited photos) · details below · median 18%
Observations
None noted in the photographs reviewed.
Heat stress
Today’s heat load
3 Oct 2026 · Alert Level 1
5-year thermal stress load
5-year mean max. degree heating weeks (DHW)
2021–2025
NOAA Coral Reef Watch — Windward 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 infoWindward Caribbean Islands (NOAA CRW virtual station) · Eastern Caribbean ecoregion mean: 13.1 degree heating weeks
Photographs
66
15 shown on this page
Site summary

A naturally acidified reef off Mayreau in the Grenadines, where volcanic CO2 seeps cause extreme pH swings; it was studied in Enochs et al. 2020 and dived 16 times in 2019. The surrounding reef is dominated by sponges and gorgonians on silty pavement, with stony corals reduced to small scattered heads and thick green algal turf in often murky water. A blind computer-vision point count of 66 photos puts coral cover around 23% (median 18%).

Max. depth dived
24.0 m

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

Four other CRD dive sites within 5 km shown in orange — click a marker to open its page.

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Photo credit & attribution

Site description

Setting

F1, the frame Anderson labels 'CO2 seep', shows the seep itself: two distinct strings of gas bubbles rising off a dark, undercut rocky outcrop, one from the shaded left flank and one from the middle of the mound, with small fish holding station in the plume. Visibility is poor and the water is green.

General benthic features

The pavement around it is a striking mosaic of magenta and rose coralline-crusted rubble and plates with yellow-brown turf between - crustose coralline algae and turf, not stony coral, hold this ground. The remaining frames (F3-F10) are the working plot. Low, silt-dusted carbonate pavement and cobble runs out flat, carpeted in dark brown and olive algal turf with clean white sand pockets in the hollows, and it is studded with survey markers: numerous magenta and red flagging tags, blue and yellow tags and white pins staked across the bottom, so densely in F4, F6, F7 and F8 that the plot layout itself is the subject. Small brown mounding and encrusting coral heads sit among the markers - discrete domes 10-30 cm across in F3, F6, F7 and F8, some crusted and partly overgrown - along with small sponges and encrusting growth on the harder blocks. This is a sparse, low-relief, turf-, and rubble-dominated bottom, not a coral framework. F5 shows a diver working head-down over the tagged plot, which gives the scale: the markers cover a patch of a few meters across. F2 is the equipment frame - a coiled yellow hose or line and dark gear resting on a heavily turf-covered pavement in very murky water. F9, his 'pseudo-mosaic', is the same plot shot near-vertically for photomosaic purposes, and F10 is a general 'vent site' overview of tagged pavement and rubble.

Coral cover

Stressors

No corallivores evident.

Comparisons with other data

No other surveys have been conducted at this site to date. Within 5 km, twenty independent stations recorded 1.2–44% hard coral cover between 1999 and 2019; the nearest, XL Catlin Seaview Survey at transect 22017, 0.16 km away, read 8.5% in 2013.

Other notes

Frame-level account of 10 frames documenting the seep and the marked study plot rather than the wider reef. Colonies here are tagged and the plot is marked out with numbered flagging, as expected for a vent-to-control gradient study; no tag or sample codes are reported, as they are not meaningful.

CV model comparison

Mean 23%, median 18% across 66 photos.
More infoThe mean is above the median because portraits of the sampled Orbicella, Montastraea and Porites colonies sit beside wide reef and gear shots; the photos documented sampled corals and are not a random benthic survey. 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 edited photographs; no other computer-vision method has been run on them yet.
More infoNo diver transect exists for this trip, so treat the value as indicative: no computer-vision method yet estimates coral cover accurately on new images.
MethodHard-coral cover (%)
Claude (edited photos)23.0

Independent surveys nearby

Data availability near this site
Agency / programYear(s)Stations / distanceLink
AGRRA2015–20198 stations, 2.34–4.79 kmRecords ↓
Literature: Deschamps et al. 200319992 stations, 3.63 kmRecords ↓
Reef Check2005–20074 stations, 2.13–3.44 kmRecords ↓
XL Catlin Seaview Survey20136 stations, 0.16–3.92 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%12%24%36%48%199920092019Literature: Deschamps et al. 2003 1999: 30%Literature: Deschamps et al. 2003 1999: 40%Reef Check 2005: 10%Reef Check 2005: 14%Reef Check 2005: 24%Reef Check 2007: 11%Reef Check 2007: 16%Reef Check 2007: 19%Reef Check 2007: 31%XL Catlin Seaview Survey 2013: 1.2%XL Catlin Seaview Survey 2013: 5.4%XL Catlin Seaview Survey 2013: 6.1%XL Catlin Seaview Survey 2013: 7.5%XL Catlin Seaview Survey 2013: 8.5%XL Catlin Seaview Survey 2013: 11%AGRRA 2015: 1.5%AGRRA 2015: 3.0%AGRRA 2015: 5.6%AGRRA 2015: 12%AGRRA 2015: 34%AGRRA 2018: 8.3%AGRRA 2018: 11%AGRRA 2018: 12%AGRRA 2018: 44%AGRRA 2019: 11%AGRRA 2019: 13%Gonzalez-Rivero et al. (2019) 2013: 8.6%Coral Reef Diagnostics 2019: 23%Year-averaged across all programs: no detectable trend (-0.79 pp per year, not separable from zero; 7 years)
Literature: Deschamps et al. 2003 Reef Check XL Catlin Seaview Survey AGRRA Gonzalez-Rivero et al. (2019) Coral Reef DiagnosticsYear-average (no detectable trend)

Within 5 km, 20 independent survey stations recorded hard coral cover in 26 records between 1999 and 2019. Of the 6 stations surveyed in more than one year, 5 increased and 1 changed by less than 5 percentage points between their first and latest surveys. The longest record, Petit Rameau (AGRRA, 2.34 km away), went from 34% in 2015 to 44% in 2018. The most recent nearby survey is from 2019, so these values predate recent heat stress. This site's own estimate (23%) sits within the range of these surveys (1.2–44%); 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; AGRRA uses benthic point-intercept transects, reported here as live coral cover; 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 range is shown. Station names are not dive-site names.

Show all 20 independent survey records
Independent survey data near this site
AgencySite / locationDateHard coral cover (%)DistanceLink
Literature: Deschamps et al. 2003Horseshoe Reef fore reef, Tobago Cays Marine Park [3-4 m]199930%3.63 km—
Literature: Deschamps et al. 2003Horseshoe Reef fore reef, Tobago Cays Marine Park [9-11 m]199940%3.63 km—
Reef CheckPetit Bateau2005–200714–19% (2 surveys)2.13 km—
Reef CheckPetit Tabac2005–200710–11% (2 surveys)3.03 km—
Reef CheckHorseshoe Reef Back Reef2005–200724–31% (2 surveys)3.14 km—
Reef CheckHorseshoe (outside)200716%3.44 km—
XL Catlin Seaview Surveytransect 2201720138.5%0.16 kmdoi:10.14264/uql.2019.930
XL Catlin Seaview Surveytransect 2201820136.1%0.24 kmdoi:10.14264/uql.2019.930
XL Catlin Seaview Surveytransect 22019201311%0.25 kmdoi:10.14264/uql.2019.930
XL Catlin Seaview Surveytransect 2201620137.5%2.60 kmdoi:10.14264/uql.2019.930
XL Catlin Seaview Surveytransect 2201420135.4%2.89 kmdoi:10.14264/uql.2019.930
XL Catlin Seaview Surveytransect 2201520131.2%3.92 kmdoi:10.14264/uql.2019.930
AGRRAPetit Rameau2015–201834–44% (2 surveys)2.34 km—
AGRRAHorseshoe REEF-SE2015–20185.6–11% (2 surveys)2.92 km—
AGRRAHorseshoe Reef MPA Site201512%3.30 km—
AGRRAWorld's End Reef-S2015–20183.0–8.3% (2 surveys)4.56 km—
AGRRANE Palm Island20151.5%4.79 km—
AGRRAHorseshoe Reef MPA site201812%3.30 km—
AGRRATaiChi Reef201913%3.10 km—
AGRRAHorse Shoe Reef201911%3.32 km—

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. Enochs IC, Formel N, Manzello D, Morris J, Mayfield AB, Boyd A, et al. (2020). Coral persistence despite extreme periodic pH fluctuations at a volcanically acidified Caribbean reef. Coral Reefs 39:523-528. DOI
  2. Deschamps A, Desrochers A, Klomp KD (2003). St. Vincent. A Rapid Assessment of the Horseshoe Reef, Tobago Cays Marine Park, St. Vincent, West Indies (Stony Corals, Algae and Fishes). Atoll Research Bulletin 496:438-459. DOI
  3. Gonzalez-Rivero M, et al. (2019). Seaview Survey photo-quadrat and image classification dataset. The University of Queensland (UQ eSpace) data collection. DOI