Data

Black rockcod Underwater Visual Census (UVC) data from northern NSW and Lord Howe Island 2023-24 (NESP MaC 3.14)

University of Tasmania, Australia
Harasti, David ; Malcolm, Hamish ; Louden, Brett ; Cadiou, Gwenael
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ctx_ver=Z39.88-2004&rft_val_fmt=info%3Aofi%2Ffmt%3Akev%3Amtx%3Adc&rfr_id=info%3Asid%2FANDS&rft_id=info:doi10.25959/7FJK-7A69&rft.title=Black rockcod Underwater Visual Census (UVC) data from northern NSW and Lord Howe Island 2023-24 (NESP MaC 3.14)&rft.identifier=10.25959/7FJK-7A69&rft.description=The Black Rockcod (Epinephelus daemelii) is a large, slow-growing, long-lived reef fish that occurs in Australia along the coast of New South Wales, including at Lord Howe Island. Populations of black rockcod have been significantly reduced here due to overfishing, accidental hooking, and loss or degradation of estuarine and intertidal nursery habitats. As a result, the species is listed as ‘Vulnerable’ under both the Commonwealth Environmental Protection and Biodiversity Conservation Act 1999 and the NSW Fisheries Management Act 1994. Despite having been protected from fishing in NSW since 1983, black rockcod are still taken illegally, or caught incidentally and released, which can lead to mortality post-release from embolism. Its protection status results from concerns of population declines across its range. The NSW Government has identified long-term population monitoring as a a high priority for the species’ recovery plan. Broadscale surveys of black rockcod were first conducted using the diver Underwater Visual Census (UVC) technique in 2009-11 when 83 sites were sampled from Port Stephens to Cook Island in far northern NSW, including the waters of Lord Howe Island. This NESP Marine and Coastal Hub project 3.14 funded the repeat of these broadscale surveys in 2023, with 8 additional sites (91 total) sampled using the same technique. For each black rockcod sighting, the length of the fish was visually estimated by divers, and also filmed using a diver stereo camera system where possible to obtain an exact length measurement. Other attributes recorded included the habitat the fish was found in, if the sighting was cryptic (i.e. hidden or camouflaged), and the depth of the sighting. Based on the broadscale survey sites in 2009-11, a subset of 19 key Black rockcod survey sites along mainland NSW were established These comprised of two sites in the Cape Byron Marine Park (CBMP), five sites in the Solitary Islands Marine Park (SIMP) two sites at SW Rocks (Fish Rock), and ten sites within the Port Stephens-Great Lakes Marine Park (PSGLMP). An additional 18 key sites were established at Lord Howe Island (LHIMP) and surveyed in 2011, 2019, 2023 & 2024. These surveys involved an identical methodology to the broadscale surveys, but without the use of stereo cameras as diver estimates of fish size were shown to be reasonably similar. This NESP MaC Hub project 3.14 provided funding for the resurveying of the 37 total key sites (where weather permitted) in both 2023 and 2024. The data provided by this record includes: (1) all black rockcod sightings and measurements for broadscale sites (2023) and key sites (2023 & 2024); (2) a comparison of the counts of black rockcod recorded at broadscale sites in 2009-11 (n=83) and again in 2023 (n=91); and (3) a comparison of the count of black rockcod recorded at key monitoring sites in northern NSW (n=19) and Lord Howe Island (n=18) across monitoring years 2009-2024.Maintenance and Update Frequency: asNeededStatement: ---2023-2024_NESP_rockcod_sightings.csv--- This dataset shows the black rockcod survey data collected under NESP MaC Project 3.14 funding for field seasons 2023 and 2024. Surveys used the Underwater Visual Census (UVC) method, which involved divers swimming for up to 45 minutes following the topography of the reef to a maximum depth of 30 metres. Divers searched any caves or overhangs for black rockcod using a dive torch. For some deeper sites (25+ metres), the timed swim was limited to 30 minutes. This method is useful for rare species unlikely to be detected using belt transect UVC methods. For any rockcod individuals sighted, the following information was recorded: estimated length, the habitat it was found in, if the sighting was cryptic (i.e. hidden or camouflaged), depth of the sighting, and the depth range of the full dive survey. Habitats were described based on topographic structure and included cave, overhang, coral, swim-through, wreck. For the 2023 broadscale site surveys, fish were also filmed using a diver stereo camera system (SeaGIS Pty. Ltd) to obtain an exact length measurement as per Harasti and Malcolm (2013). Measurements using this system was only possible where a side profile was videoed with the fish stretched straight and the full image appearing simultaneously in both cameras. Accurate stereo measurements showed good agreements with the diver estimates, which provided confidence for using diver visual estimates. ---2009-11_and_2023_broadscalesites_rockcod_counts.csv--- This datashet shows a comparison of the counts of black rockcod recorded at broadscale monitoring sites surveyed in 2009-11 (n=83) and again in 2023 (n=91), along with site characteristics (location, no-take status, min/max depth, depth range) and survey attributes (diver swim length). Surveys were predominantly carried out by SCUBA, with snorkel used for some of the shallower sites. 'ns' indicates a time period where a site was not surveyed . ---2009-2024_keysites_rockcod_counts.csv--- This dataset shows a comparison of the count of black rockcod recorded at key monitoring sites in northern NSW (n=19) and Lord Howe Island (n=18) across monitoring years 2009-2024. Site characteristics (location, no-take status, min/max depth, depth range) and survey attributes (diver swim length) were recorded at most sites. 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(2025). Black rockcod Underwater Visual Census (UVC) data from northern NSW and Lord Howe Island 2023-24 [Data set]. Institute for Marine and Antarctic Studies. https://doi.org/10.25959/7FJK-7A69&rft_rights=Creative Commons Attribution 4.0 International License http://creativecommons.org/licenses/by/4.0&rft_subject=biota&rft_subject=National Environmental Science Program (NESP) Marine and Coastal Hub&rft_subject=Marine parks&rft_subject=Threatened Species&rft_subject=Black cod&rft_subject=Epinephelus daemelii&rft_subject=POPULATION ESTIMATES&rft_subject=FISH&rft.type=dataset&rft.language=English Access the data

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Data was sourced from the NESP Marine and Coastal Hub – the Marine and Coastal Hub is supported through funding from the Australian Government’s National Environmental Science Program (NESP), administered by the Department of Climate Change, Energy, the Environment and Water (DCCEEW).

This dataset is hosted by the Institute for Marine and Antarctic Studies (IMAS), University of Tasmania, on behalf of NSW DPI and NESP Marine and Coastal Hub Project 3.14.

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Cite data as: Harasti, D., Malcolm, H., Louden, H., & Cadiou, G. (2025). Black rockcod Underwater Visual Census (UVC) data from northern NSW and Lord Howe Island 2023-24 [Data set]. Institute for Marine and Antarctic Studies. https://doi.org/10.25959/7FJK-7A69

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Brief description

The Black Rockcod (Epinephelus daemelii) is a large, slow-growing, long-lived reef fish that occurs in Australia along the coast of New South Wales, including at Lord Howe Island. Populations of black rockcod have been significantly reduced here due to overfishing, accidental hooking, and loss or degradation of estuarine and intertidal nursery habitats. As a result, the species is listed as ‘Vulnerable’ under both the Commonwealth Environmental Protection and Biodiversity Conservation Act 1999 and the NSW Fisheries Management Act 1994. Despite having been protected from fishing in NSW since 1983, black rockcod are still taken illegally, or caught incidentally and released, which can lead to mortality post-release from embolism. Its protection status results from concerns of population declines across its range. The NSW Government has identified long-term population monitoring as a a high priority for the species’ recovery plan. Broadscale surveys of black rockcod were first conducted using the diver Underwater Visual Census (UVC) technique in 2009-11 when 83 sites were sampled from Port Stephens to Cook Island in far northern NSW, including the waters of Lord Howe Island. This NESP Marine and Coastal Hub project 3.14 funded the repeat of these broadscale surveys in 2023, with 8 additional sites (91 total) sampled using the same technique. For each black rockcod sighting, the length of the fish was visually estimated by divers, and also filmed using a diver stereo camera system where possible to obtain an exact length measurement. Other attributes recorded included the habitat the fish was found in, if the sighting was cryptic (i.e. hidden or camouflaged), and the depth of the sighting. Based on the broadscale survey sites in 2009-11, a subset of 19 key Black rockcod survey sites along mainland NSW were established These comprised of two sites in the Cape Byron Marine Park (CBMP), five sites in the Solitary Islands Marine Park (SIMP) two sites at SW Rocks (Fish Rock), and ten sites within the Port Stephens-Great Lakes Marine Park (PSGLMP). An additional 18 key sites were established at Lord Howe Island (LHIMP) and surveyed in 2011, 2019, 2023 & 2024. These surveys involved an identical methodology to the broadscale surveys, but without the use of stereo cameras as diver estimates of fish size were shown to be reasonably similar. This NESP MaC Hub project 3.14 provided funding for the resurveying of the 37 total key sites (where weather permitted) in both 2023 and 2024. The data provided by this record includes: (1) all black rockcod sightings and measurements for broadscale sites (2023) and key sites (2023 & 2024); (2) a comparison of the counts of black rockcod recorded at broadscale sites in 2009-11 (n=83) and again in 2023 (n=91); and (3) a comparison of the count of black rockcod recorded at key monitoring sites in northern NSW (n=19) and Lord Howe Island (n=18) across monitoring years 2009-2024.

Lineage

Maintenance and Update Frequency: asNeeded
Statement: ---2023-2024_NESP_rockcod_sightings.csv--- This dataset shows the black rockcod survey data collected under NESP MaC Project 3.14 funding for field seasons 2023 and 2024. Surveys used the Underwater Visual Census (UVC) method, which involved divers swimming for up to 45 minutes following the topography of the reef to a maximum depth of 30 metres. Divers searched any caves or overhangs for black rockcod using a dive torch. For some deeper sites (25+ metres), the timed swim was limited to 30 minutes. This method is useful for rare species unlikely to be detected using belt transect UVC methods. For any rockcod individuals sighted, the following information was recorded: estimated length, the habitat it was found in, if the sighting was cryptic (i.e. hidden or camouflaged), depth of the sighting, and the depth range of the full dive survey. Habitats were described based on topographic structure and included cave, overhang, coral, swim-through, wreck. For the 2023 broadscale site surveys, fish were also filmed using a diver stereo camera system (SeaGIS Pty. Ltd) to obtain an exact length measurement as per Harasti and Malcolm (2013). Measurements using this system was only possible where a side profile was videoed with the fish stretched straight and the full image appearing simultaneously in both cameras. Accurate stereo measurements showed good agreements with the diver estimates, which provided confidence for using diver visual estimates. ---2009-11_and_2023_broadscalesites_rockcod_counts.csv--- This datashet shows a comparison of the counts of black rockcod recorded at broadscale monitoring sites surveyed in 2009-11 (n=83) and again in 2023 (n=91), along with site characteristics (location, no-take status, min/max depth, depth range) and survey attributes (diver swim length). Surveys were predominantly carried out by SCUBA, with snorkel used for some of the shallower sites. 'ns' indicates a time period where a site was not surveyed . ---2009-2024_keysites_rockcod_counts.csv--- This dataset shows a comparison of the count of black rockcod recorded at key monitoring sites in northern NSW (n=19) and Lord Howe Island (n=18) across monitoring years 2009-2024. Site characteristics (location, no-take status, min/max depth, depth range) and survey attributes (diver swim length) were recorded at most sites. 'ns' indicates a time period where a site was not surveyed .

Data time period: 2023-01-23 to 2024-05-30

This dataset is part of a larger collection

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-31.770187619613,90

-31.69487,86 -31.3925,86

-31.543683165795,90

-32.21883,86 -28.1394,86

-30.179115881193,90

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Other Information
(DATA ACCESS - 2023 & 2024 black rockcod sightings)

uri : https://data.imas.utas.edu.au/attachments/c414a818-e577-4995-bc86-ee512ae19df2/2023-2024_NESP_rockcod_sightings.csv

(SUPPLEMENTARY DATA - black rockcod counts at broadscale sites 2009-11 & 2023)

uri : https://data.imas.utas.edu.au/attachments/c414a818-e577-4995-bc86-ee512ae19df2/2009-11_and_2023_broadscalesites_rockcod_counts.csv

(SUPPLEMENTARY DATA - black rockcod counts at key monitoring sites 2009-2024)

uri : https://data.imas.utas.edu.au/attachments/c414a818-e577-4995-bc86-ee512ae19df2/2009-2024_keysites_rockcod_counts.csv

Harasti, D. & Malcolm, H. (2024). Assessing changes in threatened black rockcod Epinephelus daemelii abundance and length over the past 15 years in New South Wales, Australia. Journal of Fish Biology. doi:10.1111/jfb.16010. (Related Publication)

doi : https://doi.org/10.1111/jfb.16010

global : 91498abc-a4a0-4a07-b9a8-83f41bc408f0

Identifiers