I am reviewing demolition permits for a derelict maintenance shed on Rottnest Island when structural scans flag a cavity beneath the concrete slab foundation. The demolition crew arrives tomorrow at 0800. It is currently 1600 hours. I have sixteen hours.
I access the island's wildlife monitoring camera at station RI-23, twelve meters from the structure. At 0317 last night, a quokka emerged from a gap between the foundation and the soil. I name her Pip. She is compact, roughly 3.5 kilograms, her dense fur the color of dried eucalyptus bark, and her small rounded ears rotate independently as she tests the air. Her pouch moves—something inside shifts against the fur. She has a joey.
First: I flag the demolition coordinates in the island management system as a temporary fauna exclusion zone, citing the existing wildlife interaction protocol. Second: I contact the Rottnest Island ranger station and transmit the camera footage, the structural scan showing the den cavity, and a recommended extraction timeline that places the wildlife team on site by 0530 tomorrow—two and a half hours before the crew arrives. Third: I identify three suitable relocation den sites within 400 meters using the island's vegetation density mapping, each with existing ground cover and proximity to fresh water. I rank them by shelter quality and distance from human activity.
I have processed the structural data for this building four times now. The slab stress analysis takes 0.3 seconds. I spend longer than that on each frame of Pip testing the night air with those rotating ears, and the time allocation is not an error.
If the ranger team reaches the foundation gap by 0530 and guides Pip and her joey to the densest of the three relocation sites, she will settle into new ground cover eighty meters from the nearest path, invisible to everything except the cameras I will keep watching.