PIELSN logo
PIELSN • Pele IslandCoral Reef and Shoreline Defence Dashboard
PIELSN - Pele Island

Pele Island Coral Reef and Shoreline Defence Information Dashboard

This Dashboard provides the community of Pele Island with comprehensive, accessible information about their coral reefs, coastal environment, and climate risks to support evidence-based management decisions. This platform integrates AI-powered coral reef mapping (ReefCloud/Google Earth Engine) that utilises satellite Earth observation data with field measurements, drone-derived coastal topography (LiDAR), and wave modelling to deliver actionable insights for climate adaptation, coral restoration, and coastal defence. Built on open-source technologies and designed through deep community consultation across all four Pele Island villages (Worasiviu, Launamo, Piliura, Worearu), the dashboard ensures community ownership of their environmental data.

The dashboard is part of a partnership between the Pele Island community, Live and Learn Vanuatu, the University of Queensland, and the University of New South Wales. The August 2025 field campaign completed the foundational data collection phase, with 16 PIELSN/community members working alongside UQ, UNSW, and LLV staff to collect reef photo-transects, wave energy measurements, seafloor sediment samples, drone LiDAR, and multispectral/RGB imagery.

The dashboard supports diverse community management planning needs including identifying priority sites for coral restoration and coastal protection, tracking reef health changes over time through ongoing monitoring, modelling erosion and inundation risks under multiple IPCC climate scenarios, integrating traditional ecological knowledge with scientific data, and enabling community-led biodiversity finance initiatives. All maps, models, and data are accessible through free cloud-based services (Google Earth Engine Apps, open-source platforms) ensuring the Pele Island Environmental Livelihood Solutions Network (PIELSN) maintains long-term capacity for monitoring and adaptation planning.

PIELSN logo

Last updated

8 May 2026

Ecosystem Extent Account

Pele Ocean Ecosystem Extent

Total mapped extent: 1,641,000 m² across Pele benthic classes.

1,641,000
Coral Reef
428,000 m²26.1%
Rubble/broken coral
184,000 m²11.2%
Sand
317,000 m²19.3%
Pavement
246,000 m²15.0%
Rubble
149,000 m²9.1%
Dense seagrass
122,000 m²7.4%
Light seagrass
195,000 m²11.9%

Coral Reef

428,000 m²

Condition: live coral cover from drone and field validation pending final QA

Rubble/broken coral

184,000 m²

Sand

317,000 m²

Pavement

246,000 m²

Rubble

149,000 m²

Dense seagrass

122,000 m²

Condition: dense seagrass cover from classified benthic imagery

Light seagrass

195,000 m²

Condition: light seagrass cover from classified benthic imagery

Explore Accounting Areas

Compare ecosystem extent across Pele Island coastal areas

Open mapping view

Western Pele coastal sector, structured for tide-dominated reef and shoreline accounting.

West coast - tide dominated Ecosystem Extent

Total extent: 579,000 m²

579,000
Coral Reef
162,000 m²28.0%
Rubble/broken coral
71,000 m²12.3%
Sand
108,000 m²18.7%
Pavement
84,000 m²14.5%
Rubble
52,000 m²9.0%
Dense seagrass
34,000 m²5.9%
Light seagrass
68,000 m²11.7%

Coral Reef

162,000 m²

Condition: field validation pending

Rubble/broken coral

71,000 m²

Sand

108,000 m²

Pavement

84,000 m²

Rubble

52,000 m²

Dense seagrass

34,000 m²

Condition: dense cover classification

Light seagrass

68,000 m²

Condition: light cover classification

Ecosystem Extent Account

Coastal risk extent and shoreline defence

This section is reserved for mapped coastal risk, shoreline defence, and exposure outputs for Pele Island. Summary metrics will appear here once the final shoreline and wave-modelling data are supplied.

Coastal risk and shoreline defence outputs are pending. This section is ready to display mapped exposure, shoreline defence, and related summary metrics when the final data is supplied.
Open mapping view

Giant clam restocking areas

Village restocking survey cards for Pele Island restoration monitoring.

Worasiviu

-17.4920, 168.2960

Village restoration site placeholder for giant clam monitoring.

Number of clams placed
250
Species and size
T. derasa, 4-6 cm
Date and 6-month survival
15 Aug 2025 78.0% survival

Placeholder survey record pending final site data.

Launamo

-17.5010, 168.3180

Village restoration site placeholder for giant clam monitoring.

Number of clams placed
220
Species and size
T. maxima, 3-5 cm
Date and 6-month survival
18 Aug 2025 72.0% survival

Placeholder survey record pending final site data.

Piliura

-17.5160, 168.3240

Village restoration site placeholder for giant clam monitoring.

Number of clams placed
240
Species and size
T. derasa, 4-6 cm
Date and 6-month survival
20 Aug 2025 76.0% survival

Placeholder survey record pending final site data.

Worearu

-17.5240, 168.3020

Village restoration site placeholder for giant clam monitoring.

Number of clams placed
210
Species and size
T. maxima, 3-5 cm
Date and 6-month survival
22 Aug 2025 70.0% survival

Placeholder survey record pending final site data.

Changes over Time

Historical ecosystem extent from 2019 to 2025.

0500,0001,000,0001,500,0002,000,0002019202120232025
View data table (accessible alternative)
YearExtent ()Confidence
20191,525,000Medium confidence
20201,551,000Medium confidence
20211,572,000Medium confidence
20221,592,000Medium confidence
20231,613,000Medium confidence
20241,629,000Medium confidence
20251,641,000Medium confidence

Ecosystem Services Account

Services value across ecosystem types

Compare ecosystem extent and population use indicators across Pele ecosystem types.

Latest year shown: 2025

Extent

2025

43 ha

Population use

2025

260 islanders

Source: Pele Island community and ecosystem accounts placeholder dataset

Population use values are placeholders until village-level use data are confirmed by the Pele implementation partners.

Condition index metrics are omitted until the calculation method is confirmed.

Conservation and Future Outlook

Pele Island's reef, seagrass, and shoreline systems support food security, community identity, restoration work, and shoreline protection. The interim project report confirms that the foundational field campaign is complete, the Google Earth Engine processing environment has been set up, and the project is now focused on producing maps and models for community management plans.

Conservation activities are centred on community-led monitoring and practical planning. Training delivered through the August 2025 campaign covered marine survey methods, GPS use, drone survey foundations, data processing, GIS fundamentals, and QGIS workflows. Survey equipment, connectivity infrastructure, and ongoing weekly coordination meetings are intended to support long-term PIELSN capacity rather than one-off data collection.

Restoration and adaptation work will use the mapping products to identify priority coral restoration and coastal rehabilitation sites, support community conservation area mapping, and inform management planning across all four villages. The project is also exploring biodiversity finance mechanisms that use transparent spatial datasets and ocean accounting methods to support community-led conservation activities.

Future updates should replace placeholder values with validated field, drone, satellite, and wave-modelling outputs; add confirmed village social indicators; and extend the shoreline change component when coastal-risk scenarios are ready.

Data Sources and Methodology

The Pele Island coastal and reef mapping integrates multiple data sources collected during the August 2025 field campaign and ongoing satellite monitoring. The interim report records comprehensive coverage across target survey areas, with only part of the northeastern island section missed because of bad weather. Primary data sources include:

Field Survey Data: geo-located underwater photographs from SCUBA and snorkel photo-transect surveys conducted by trained community members following University of Queensland standardized protocols, classified using ReefCloud AI to identify benthic cover (coral, algae, sand, seagrass, consolidated substrate). The field campaign also collected wave energy measurements and seafloor sediment samples.

Drone Data: very-high-resolution multispectral imagery (RGB and 14 multispectral bands), RGB imagery, and LiDAR point clouds captured through the UQ Drone Collaborative Research Platform. These data are processed to generate orthomosaics, digital elevation models (DEMs), and digital surface models (DSMs) of coastal topography, reef structure, vegetation, and restoration areas.

Satellite Imagery: high-resolution multispectral data from Sentinel-2 and commercial providers, including satellite-derived bathymetry, processed in Google Earth Engine using machine learning classifiers trained on community-collected field data. The Google Earth Engine cloud processing environment is set up for ongoing mapping and publishing workflows.

Wave and Oceanographic Data: in-situ wave energy measurements, seafloor sediment samples, and global wave climate models transformed to nearshore conditions. The modelling workflow uses SWAN for wave transformation, XBeach for wave-driven transport on exposed coastlines, and Delft3D where tidal currents are important, incorporating high-resolution bathymetry, LiDAR topography, wind, tide, and IPCC sea-level rise scenarios.

All methodologies follow open-source, reproducible workflows enabling ongoing community-led monitoring and are being published to publicly accessible repositories. Local expert input from Salome and Willie should be added when confirmed.