Coral Reef Diagnostics

Bonaire - Karpata

Reef Check Foundation
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05
Coral Reef Diagnostics
Photo: Anderson Mayfield/Coral Reef Diagnostics
Country
Survey date(s)
2017-02-21
Coordinates
12.2195, -68.3521
Position from the published dive-site listing for Karpata; other online dive-site maps agree within 20 m; no GPS fix was logged on the dive.
Coral cover
36%
Claude computer vision (41 edited photos) · other methods below · median 38%
Observations
None tagged; see Stressors below
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
NOAA Coral Reef Watch — Aruba, Curacao, and Bonaire 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 infoAruba, Curacao, and Bonaire (NOAA CRW virtual station)
Photographs
48
42 shown on this page; 49 analyzed
Site summary
Read this summary in:

A shore dive down a concrete stairway on Bonaire's northwest coast onto an unbroken carpet of boulder star coral, with living elkhorn coral in the shallows, a resting hawksbill turtle, and dense schools of sergeant majors and chromis. Most colonies are well pigmented, though one large brain coral shows extensive old partial die-off.

Max. depth dived
36.3 m
Water temp. during survey
26.7°Cii
-1.2°C vs the 2017 mean sea temperature (27.9°C)
ii From 1 logged dive at this site.
Bottom time
46 min
in at 14:17

Ten 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.

6 of the 42 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

A shore dive down a concrete stairway on Bonaire's northwest coast, entering a slope built on an extensive, unbroken carpet of boulder star coral heads with patches of elkhorn coral in the shallows and gorgonian sea plumes scattered among the mounds (e.g., Image 4, Image 5).

General benthic features

Many of these scenic frames show high apparent live-coral occupancy, especially in shallow fields of large massive and lobate star-coral forms (e.g., Image 2).

The set also records reef-wall relief, brain and plating corals, octocorals, and living Acropora palmata (e.g., Image 1, Image 3).

Coral cover

Stressors

No widespread bleaching signal is visible. Most colonies retain substantial pigmented live tissue. One frame clearly shows a large brain coral with extensive central old partial mortality and encrusted/exposed skeleton, demonstrating meaningful colony-level loss despite otherwise coral-dense scenes. A single time point cannot establish whether the margin was active in 2017. No corallivores were evident.

Fish and other fauna

A hawksbill turtle rested on the reef and dense schools of sergeant majors and blue chromis hovered over the coral (e.g., Image 36).

Turtles, schooling fishes, and blue tangs are conspicuous.

Comparisons with other data

Stokes et al. 2010 surveyed this site (Karpata (Bonaire Marine Park mooring) [2008 - 5 m]) in 2008, 0.08 km from the pin. Within 5 km, ten independent stations recorded station-year means of 20–60% hard coral cover between 1999 and 2017; the nearest, Stokes et al. 2010 at Karpata (Bonaire Marine Park mooring) [2008 - 5 m], 0.08 km away, read 36% in 2008.

CV model comparison

Mean 36%, median 38% across 41 photos.
More infoA few low-cover photos (sand, rubble, or open bottom) pull the mean down; 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 infoOther rows are for comparison only and are never averaged. No diver transect exists for these photos, so agreement between rows is not accuracy.
MethodHard coral cover (%)Photos (n) ± SE
CoralSCOP edited32.3n = 49 · SE 2.6
Claude (edited photos)35.6n = 41 · SE 2.9

CoralSCOP (edited photos) reads 32.3%, within 3.3 pp of Claude's blind point count (35.6%).

Independent surveys nearby

Data availability near this site
Agency / programYear(s)Stations / distanceLink
Kramer & Bischof 200319991 station, 0.08 kmRecords ↓
Reef Check2000–20031 station, 0.81 kmRecords ↓
Steneck et al. (2019)2004–20172 stations, 0.23–1.95 kmRecords ↓
Stokes et al. 201020083 stations, 0.08 kmRecords ↓
XL Catlin Seaview Survey20133 stations, 0.09–4.29 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%15%30%45%60%199920082017Kramer & Bischof 2003 1999: 44%Reef Check 2000: 34%Reef Check 2001: 24%Reef Check 2002: 26%Reef Check 2003: 28%Steneck et al. (2019) 2004: 46%Steneck et al. (2019) 2005: 47%Steneck et al. (2019) 2007: 44%Steneck et al. (2019) 2011: 39%Steneck et al. (2019) 2013: 40%Steneck et al. (2019) 2013: 45%Steneck et al. (2019) 2015: 47%Steneck et al. (2019) 2015: 50%Steneck et al. (2019) 2017: 54%Steneck et al. (2019) 2017: 60%Stokes et al. 2010 2008: 31%Stokes et al. 2010 2008: 36%Stokes et al. 2010 2008: 42%XL Catlin Seaview Survey 2013: 20%XL Catlin Seaview Survey 2013: 25%XL Catlin Seaview Survey 2013: 26%Coral Reef Diagnostics 2017: 36%Year-averaged across all programs: illustrative only; the programs differ in stations and method, so no trend is claimed (13 years)
Kramer & Bischof 2003 Reef Check Steneck et al. (2019) Stokes et al. 2010 XL Catlin Seaview Survey Coral Reef DiagnosticsYear-average (illustrative only, programs differ)

Within 5 km, 10 independent survey stations recorded hard coral cover in 59 records between 1999 and 2017. Of the 3 stations surveyed in more than one year, 1 declined (by 6.0 points) and 2 increased (by 9.0–14 points) between their first and latest surveys. The longest record, Karpata (Steneck et al. 2019, 0.23 km away), went from 46% in 2004 (mean of 8 records) to 60% in 2017 (mean of 4 records). The most recent nearby survey is from 2017, so these values predate recent heat stress. This site's own estimate (36%) sits within the range of these station-year means up to 2 km away (24–60%); 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
Kramer & Bischof 2003Karpata [10 m]199944%0.08 km—
Reef CheckKarpata Reserve2000–200324–34% (range of yearly means; 8 surveys)0.81 km—
Steneck et al. (2019)Karpata2004–201739–60% (range of yearly means; 32 records)0.23 kmdoi:10.3389/fmars.2019.00265
Stokes et al. 2010Karpata (Bonaire Marine Park mooring) [2008 - 5 m]200836%0.08 kmdoi:10.5479/si.00775630.582.1
Stokes et al. 2010Karpata (Bonaire Marine Park mooring) [2008 - 10 m]200842%0.08 kmdoi:10.5479/si.00775630.582.1
Stokes et al. 2010Karpata (Bonaire Marine Park mooring) [2008 - 15 m]200831%0.08 kmdoi:10.5479/si.00775630.582.1
XL Catlin Seaview Surveytransect 17039201325%0.09 kmdoi:10.14264/uql.2019.930
Steneck et al. (2019)No-Dive Reserve2013–201745–54% (range of yearly means; 12 records)1.95 kmdoi:10.3389/fmars.2019.00265
XL Catlin Seaview Surveytransect 17038201320%2.33 kmdoi:10.14264/uql.2019.930
XL Catlin Seaview Surveytransect 17046201326%4.29 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. Kramer P, Bischof BG (2003). AGRRA Data. Assessment Tables for Abaco, Bahamas (Fishes), Lighthouse Belize(Corals, Algae, Fishes) and Bonaire, Netherlands Antilles (Corals, Algae, Fishes). Atoll Research Bulletin 496:590-597. DOI
  2. Steneck RS, Arnold SN, Boenish R, de León R, Mumby PJ, Rasher DB, et al. (2019). Managing Recovery Resilience in Coral Reefs Against Climate-Induced Bleaching and Hurricanes: A 15 Year Case Study From Bonaire, Dutch Caribbean. Frontiers in Marine Science 6:265. PDF
  3. Stokes MD, Leichter JJ, Genovese SJ (2010). Long-term declines in coral cover at Bonaire, Netherlands Antilles. Atoll Research Bulletin 582:1-21. DOI
  4. Gonzalez-Rivero M, et al. (2019). Seaview Survey photo-quadrat and image classification dataset. The University of Queensland (UQ eSpace) data collection. DOI