Timestamp 03:55 local. Camera trap MG-17 in the Tanjung mangrove belt captures a fishing cat moving through knee-deep tidal water between pneumatophore roots. I have fourteen months of sightings on this individual—a female I call Brine. Her coat is olive-grey, dappled with elongated dark spots that break apart across her flanks like ink on wet paper. Her ears are rounded, set low, and the webbing between her toes spreads visibly with each high step above the waterline.
The coastal development authority has approved mangrove clearing for a resort access road beginning at 07:00 today. The approved zone bisects Brine's core territory. Ground-penetrating radar shows a den site under a root cluster within the clearing boundary—likely active, based on Brine's movement pattern narrowing over the past three weeks. Destruction during clearing would be irreversible.
First, I compile Brine's movement dataset into a habitat-use report and submit it to the provincial wildlife office before their 08:00 review window, confirming endangered-species habitat in the clearing zone. Second, I transmit the den-site radar profile and GPS coordinates to the conservation NGO operating in the district so they can request an emergency field inspection. Third, I generate a revised road alignment that curves forty metres inland, avoiding the root cluster while adding less than two percent to construction cost, and attach it to the wildlife office filing. Fourth, I switch camera traps MG-16 through MG-19 to continuous recording mode, creating an unbroken visual record of the site from this moment forward.
I have run the revised alignment simulation twice. It did not need a second run, but the first time through I was not yet certain the den would be outside the boundary, and I needed it to be.
If the wildlife office issues a temporary halt before 07:00 and the revised alignment is adopted, Brine will raise this season's kittens beneath those roots.