This dataset contains measurements of predation rates, predator abundance, and environmental variables collected in September 2023 across 18 permanent 20 × 20 m study plots in tropical rainforest of the Cassowary Coast Region, Wet Tropics World Heritage Area, North Queensland, Australia. Predation was quantified using 360 artificial plasticine caterpillars exposed for seven days and inspected for predator attack marks, alongside concurrent pitfall trapping of ground-dwelling arthropods (ants, carabid beetles, and crickets). Environmental data include tree and vine stem counts, species identifications, basal area, aboveground biomass estimates, vine-to-tree ratios, leaf area index from hemispherical photographs, litter depth, and coarse woody debris surveys. These data were collected following standardised ecological protocols to support analysis of predator–prey interactions, vegetation structure, and rainforest disturbance dynamics.
Credit
We at TERN acknowledge the Traditional Owners and Custodians throughout Australia, New Zealand and all nations. We honour their profound connections to land, water, biodiversity and culture and pay our respects to their Elders past, present and emerging.
Purpose
The data were collected to quantify predation pressure and predator activity in relation to rainforest vegetation structure and disturbance history. Artificial caterpillars provide a standardised measure of relative predation rates across broad predator groups, while pitfall trapping captures the abundance of ground-dwelling arthropod predators. Vegetation and environmental measurements, including tree and vine structure, aboveground biomass, litter depth, and coarse woody debris, were collected to characterise habitat conditions and allow testing of how forest composition and structural complexity influence predator–prey interactions. Together, these data provide a baseline for understanding the ecological role of predators in disturbed and recovering tropical rainforests of the Wet Tropics region.
Lineage
Environmental data were collected from rainforest plots using standardised forest inventory methods. All trees and climbing plants with diameter at breast height (DBH) ≥ 1 cm were measured, with vines classified as either woody lianas or climbing monocots (including rattans). Basal area, stem density, and vine-to-tree ratios were calculated per plot. Tree aboveground biomass was estimated using a pan-tropical allometric equation with a standardised wood density value. Canopy structure was assessed from hemispherical photographs to calculate leaf area index (LAI). Litter depth was measured at multiple points per plot and averaged, and coarse woody debris was quantified along transects. All variables were quality checked for consistency prior to analysis.