Data

Testing the effects of scale on benthic habitat modelling in the South-west Corner Marine Park (NESP MaC 2.3)

University of Tasmania, Australia
Langlois, Tim ; Monk, Jacquomo ; Spencer, Claude ; Wooley, Skipton ; Flukes, Emma ; Gibbons, Brooke ; Hayes, Keith
Viewed: [[ro.stat.viewed]] Cited: [[ro.stat.cited]] Accessed: [[ro.stat.accessed]]
ctx_ver=Z39.88-2004&rft_val_fmt=info%3Aofi%2Ffmt%3Akev%3Amtx%3Adc&rfr_id=info%3Asid%2FANDS&rft_id=info:doi10.25959/2RKJ-H521&rft.title=Testing the effects of scale on benthic habitat modelling in the South-west Corner Marine Park (NESP MaC 2.3)&rft.identifier=10.25959/2RKJ-H521&rft.description=This dataset presents the results of a seafloor habitat modeling exercise for the 'Capes region' of the South-west Corner Marine Park, southern WA. The model classifies five broad habitat types (hereafter 'ecosystem components'): seagrass, macroalgae, sessile invertebrates, bare consolidated substrata, and bare unconsolidated substrata. Modeling was conducted at two spatial scales to assess the effectiveness of using broad-scale (~250 m) spatial covariates derived from bathymetry in mapping habitat classes and to compare the modelling outcomes with those obtained using finer-resolution input data. The fine-scale mapping focused on an IUCN II zone near Margaret River, using a seamless 5 m resolution multibeam bathymetry composite. The broad-scale mapping covered multiple IUCN zones, including the southwestern Geographe Australian Marine Park (AMP), the northwestern tip of the South-west Corner AMP, and the Ngari Capes WA State Marine Park. This component used the 250 m resolution 2023 AusBathyTopo grid from Geoscience Australia. Habitat maps were constructed using (1) the bathymetry data sources described above; (2) ground-truthing observations from stereo-BRUV and BOSS camera systems; and (3) Physical covariates, all smoothed to 5 m or 250 m resolution, for the fine- and broad-scale mapping, respectively. Source datasets are available from: • Geoscience Australia's eCat: https://dx.doi.org/10.26186/145281 (5 m multibeam bathymetry) and https://doi.org/10.26186/148758 (250 m DEM bathymetry) • Squidle+: http://squidle.org/geodata/explore (benthic imagery annotations - see also outputs from NESP MaC Project 2.4: https://doi.org/10.25959/6G5A-3G03) • AODN Portal: https://portal.aodn.org.au/search (IMOS oceanographic datasets). This analysis uses the modelling methodology developed in NESP Project 2.1, which extended the ecosystem component modelling to include all temperate Australian shelf waters at a resolution of 250 m (https://doi.org/10.25959/BVJ7-D984). Analysing the scale effects effects of spatial covarariate inputs was undertaken by NESP Project 2.3, along with exploration of visualisation options regarding prediction certainty in consultation with Parks Australia (management end-users). Further details on sampling design for ground-truthing observations and the modelling techniques are available in the NESP MaC Project 2.1 Final Report: https://www.nespmarinecoastal.edu.au/publication/improving-seabed-habitat-predictions-for-southern-australia. A description on this specific South-west Corner case study and the spatial scale analysis is described in the NESP MaC Project 2.3 Final Report: https://www.nespmarinecoastal.edu.au/publication/improving-knowledge-transfer-to-support-australian-marine-park-decision-making-and-management-effectiveness-evaluation. A selection of mapping (WMS) services are listed in the 'Downloads & Links' section of this record. See the 'Lineage' section for a full description of the data packages available for download, and for more visualisation options.Maintenance and Update Frequency: none-plannedStatement: This modelling approach used a Bayesian implementation of a multinomial generalised linear model. Ground-truthing benthic annotations for mobile species (e.g. echinodermata) were discarded. All remaining annotations were collapsed into the five broad ecosystem components. See NESP Marine and Coastal Project 2.1 final report for a full description of the sampling design, annotation technique, and modelling approach. A key objective of this work was to compare the habitat modelled using input data at high resolution (where available), with that generated from low resolution bathymetric model data, which is readily available and has full coverage of Australian waters (see Beaman, R. (2024). AusBathyTopo (Australia) 250m 2024 - A national-scale depth model. https://dx.doi.org/10.26186/150050). A secondary objective was to evaluate two approaches for presenting model outputs to better support marine management decisions. Both modeling scales provide predicted mean probability of occurrence for each ecosystem component, while the broad-scale model also incorporates model uncertainty, allowing users to define a minimum acceptable occurrence threshold based on their specific needs. ---FINE-SCALE (5 m) MODEL--- https://data.imas.utas.edu.au/attachments/seamap_predicted_habitat/southwest_corner/finescale This approach models the mean probability of occurrence for each of the five ecosystem components (seagrass, sessile invertebrates, macroalgae, bare consolidated, bare unconsolidated) at 5 metre resolution. The data is packaged in two formats: (1) five individual raster files, each representing the mean probability of occurrence for a different ecosystem component. (2) a single 5-band raster where each band corresponds to the mean probability of occurrence for a different ecosystem component: Band 1 = bare consolidated, band 2 = macroalgae, Band 3 = seagrass, Band 4 = bare unconsolidated, Band 5 = sessile invertebrates See ReadMe file for a full description of the data package. ---BROAD-SCALE (250 m) MODEL--- https://data.imas.utas.edu.au/attachments/seamap_predicted_habitat/southwest_corner/broadscale This approach models the same five ecosystem components at 250 metre resolution and provides outputs in two complementary formats: (1) Continuous Probability Estimates Presents set of three rasters for each ecosystem component, representing: - Lower 95th credible interval (0.025 quantile): the lower bound of the predicted probability range. - Mean probability of occurrence: the central estimate based on the posterior distribution. - Upper 95th credible interval (0.975 quantile): the upper bound of the predicted probability range. (2) Thresholded Probability Estimates Presents a set of rasters capturing model certainty at 10 probability thresholds (0.000001 - 0.9) for each ecosystem component. Each raster represents a specific probability threshold (quantile) and indicates the model's certainty that a given habitat class occurs at or above that threshold. This provides a structured way to assess model confidence across different probability levels. This dual representation allows for both a continuous probability assessment and a threshold-based evaluation of model confidence across different probability levels. 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(2025). Testing the effects of scale on benthic habitat modelling in the South-west Corner Marine Park [Data set]. Institute for Coastal Marine Environment. https://doi.org/10.25959/2RKJ-H521&rft_rights=This dataset is hosted by the Institute for Marine and Antarctic Studies (IMAS), University of Tasmania, on behalf NESP Marine and Coastal Hub Projects 2.1 & 2.3.&rft_rights=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).&rft_rights=Creative Commons Attribution 4.0 International License http://creativecommons.org/licenses/by/4.0&rft_subject=biota&rft_subject=environment&rft_subject=National Environmental Science Program (NESP) Marine and Coastal Hub&rft_subject=KELP FOREST&rft_subject=SPONGES&rft_subject=MACROALGAE (SEAWEEDS)&rft_subject=SEAGRASS&rft_subject=BENTHIC&rft_subject=MARINE ECOSYSTEMS&rft_subject=Environmental Science and Management not elsewhere classified&rft_subject=ENVIRONMENTAL SCIENCES&rft_subject=ENVIRONMENTAL SCIENCE AND MANAGEMENT&rft_subject=Marine and Estuarine Ecology (incl. Marine Ichthyology)&rft_subject=BIOLOGICAL SCIENCES&rft_subject=ECOLOGY&rft_subject=Conservation and Biodiversity&rft.type=dataset&rft.language=English Access the data

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Cite data as: Langlois, T., Monk, J., Spencer, C., Flukes, E., Gibbons, B., & Hayes, K. (2025). Testing the effects of scale on benthic habitat modelling in the South-west Corner Marine Park [Data set]. Institute for Coastal Marine Environment. https://doi.org/10.25959/2RKJ-H521

This dataset is hosted by the Institute for Marine and Antarctic Studies (IMAS), University of Tasmania, on behalf NESP Marine and Coastal Hub Projects 2.1 & 2.3.

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).

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Brief description

This dataset presents the results of a seafloor habitat modeling exercise for the 'Capes region' of the South-west Corner Marine Park, southern WA. The model classifies five broad habitat types (hereafter 'ecosystem components'): seagrass, macroalgae, sessile invertebrates, bare consolidated substrata, and bare unconsolidated substrata. Modeling was conducted at two spatial scales to assess the effectiveness of using broad-scale (~250 m) spatial covariates derived from bathymetry in mapping habitat classes and to compare the modelling outcomes with those obtained using finer-resolution input data. The fine-scale mapping focused on an IUCN II zone near Margaret River, using a seamless 5 m resolution multibeam bathymetry composite. The broad-scale mapping covered multiple IUCN zones, including the southwestern Geographe Australian Marine Park (AMP), the northwestern tip of the South-west Corner AMP, and the Ngari Capes WA State Marine Park. This component used the 250 m resolution 2023 AusBathyTopo grid from Geoscience Australia. Habitat maps were constructed using (1) the bathymetry data sources described above; (2) ground-truthing observations from stereo-BRUV and BOSS camera systems; and (3) Physical covariates, all smoothed to 5 m or 250 m resolution, for the fine- and broad-scale mapping, respectively. Source datasets are available from: • Geoscience Australia's eCat: https://dx.doi.org/10.26186/145281 (5 m multibeam bathymetry) and https://doi.org/10.26186/148758 (250 m DEM bathymetry) • Squidle+: http://squidle.org/geodata/explore (benthic imagery annotations - see also outputs from NESP MaC Project 2.4: https://doi.org/10.25959/6G5A-3G03) • AODN Portal: https://portal.aodn.org.au/search (IMOS oceanographic datasets). This analysis uses the modelling methodology developed in NESP Project 2.1, which extended the ecosystem component modelling to include all temperate Australian shelf waters at a resolution of 250 m (https://doi.org/10.25959/BVJ7-D984). Analysing the scale effects effects of spatial covarariate inputs was undertaken by NESP Project 2.3, along with exploration of visualisation options regarding prediction certainty in consultation with Parks Australia (management end-users). Further details on sampling design for ground-truthing observations and the modelling techniques are available in the NESP MaC Project 2.1 Final Report: https://www.nespmarinecoastal.edu.au/publication/improving-seabed-habitat-predictions-for-southern-australia. A description on this specific South-west Corner case study and the spatial scale analysis is described in the NESP MaC Project 2.3 Final Report: https://www.nespmarinecoastal.edu.au/publication/improving-knowledge-transfer-to-support-australian-marine-park-decision-making-and-management-effectiveness-evaluation. A selection of mapping (WMS) services are listed in the 'Downloads & Links' section of this record. See the 'Lineage' section for a full description of the data packages available for download, and for more visualisation options.

Lineage

Maintenance and Update Frequency: none-planned
Statement: This modelling approach used a Bayesian implementation of a multinomial generalised linear model. Ground-truthing benthic annotations for mobile species (e.g. echinodermata) were discarded. All remaining annotations were collapsed into the five broad ecosystem components. See NESP Marine and Coastal Project 2.1 final report for a full description of the sampling design, annotation technique, and modelling approach. A key objective of this work was to compare the habitat modelled using input data at high resolution (where available), with that generated from low resolution bathymetric model data, which is readily available and has full coverage of Australian waters (see Beaman, R. (2024). AusBathyTopo (Australia) 250m 2024 - A national-scale depth model. https://dx.doi.org/10.26186/150050). A secondary objective was to evaluate two approaches for presenting model outputs to better support marine management decisions. Both modeling scales provide predicted mean probability of occurrence for each ecosystem component, while the broad-scale model also incorporates model uncertainty, allowing users to define a minimum acceptable occurrence threshold based on their specific needs. ---FINE-SCALE (5 m) MODEL--- https://data.imas.utas.edu.au/attachments/seamap_predicted_habitat/southwest_corner/finescale This approach models the mean probability of occurrence for each of the five ecosystem components (seagrass, sessile invertebrates, macroalgae, bare consolidated, bare unconsolidated) at 5 metre resolution. The data is packaged in two formats: (1) five individual raster files, each representing the mean probability of occurrence for a different ecosystem component. (2) a single 5-band raster where each band corresponds to the mean probability of occurrence for a different ecosystem component: Band 1 = bare consolidated, band 2 = macroalgae, Band 3 = seagrass, Band 4 = bare unconsolidated, Band 5 = sessile invertebrates See ReadMe file for a full description of the data package. ---BROAD-SCALE (250 m) MODEL--- https://data.imas.utas.edu.au/attachments/seamap_predicted_habitat/southwest_corner/broadscale This approach models the same five ecosystem components at 250 metre resolution and provides outputs in two complementary formats: (1) Continuous Probability Estimates Presents set of three rasters for each ecosystem component, representing: - Lower 95th credible interval (0.025 quantile): the lower bound of the predicted probability range. - Mean probability of occurrence: the central estimate based on the posterior distribution. - Upper 95th credible interval (0.975 quantile): the upper bound of the predicted probability range. (2) Thresholded Probability Estimates Presents a set of rasters capturing model certainty at 10 probability thresholds (0.000001 - 0.9) for each ecosystem component. Each raster represents a specific probability threshold (quantile) and indicates the model's certainty that a given habitat class occurs at or above that threshold. This provides a structured way to assess model confidence across different probability levels. This dual representation allows for both a continuous probability assessment and a threshold-based evaluation of model confidence across different probability levels. See ReadMe file for a full description of the data package.

Notes

Credit
National Environmental Science Program (NESP) Marine and Coastal Hub
Credit
Department of Climate Change, Energy, the Environment and Water (DCCEEW), Australian Government
Credit
In addition to NESP (DCCEEW) funding, this project is matched by an equivalent amount of in-kind support and co-investment from project partners and collaborators.

Data time period: 2020-01-01 to 2024-01-30

This dataset is part of a larger collection

-34.24994,86 -33.49994,86

-33.87493897,90

text: uplimit=250; downlimit=10

Other Information
(DATA ACCESS - Explore and individually download individual data files, ReadMe etc.)

uri : https://data.imas.utas.edu.au/attachments/seamap_predicted_habitat/southwest_corner/

(DATA ACCESS - Full data package (.zip of above))

uri : https://data.imas.utas.edu.au/attachments/seamap_predicted_habitat/southwest_corner/Langlois_etal_NESP2.1_SWC_model.zip

(View & explore South-west Corner finescale (5m) model outputs in Seamap Australia)

uri : https://seamapaustralia.org/map/#e4798bf7-5535-42d7-9db8-a890123c8bfc

Interact with quantile thresholds by selecting an Ecosystem Component from the layer tab options. (View & explore South-west Corner broadscale (250m) model outputs in Seamap Australia)

uri : https://seamapaustralia.org/map/#f6c9caf9-f5a2-4c42-8b84-88dd29c6e181

(GitHub repo for South-West Corner benthos and fish survey design and analysis)

uri : https://github.com/UWA-Marine-Ecology-Group-projects/mac-swc

(Related Publication: NESP 2.1 Final Report - modelling methodology)

uri : https://www.nespmarinecoastal.edu.au/publication/improving-seabed-habitat-predictions-for-southern-australia/

(Related Publication: NESP 2.3 Final Report - scale-based analysis)

uri : https://www.nespmarinecoastal.edu.au/publication/improving-knowledge-transfer-to-support-australian-marine-park-decision-making-and-management-effectiveness-evaluation/

global : 7cb3ac61-dd39-448a-8b2f-2b9d64f153c6

Identifiers