Ecological networks are central tools for addressing habitat fragmentation, but research practice has increasingly shifted from organism-center evidence toward GIS-based mapping and structural connectivity modeling. Remote-sensing data, resistance surfaces, circuit theory and ecosystem-service layers now allow visually persuasive networks to be produced over large areas with limited fieldwork. These approaches are indispensable for broad-scale conservation planning, yet they can blur the distinction between potential connectivity and demonstrated ecological function. A mapped corridor is not necessarily a movement pathway, and structural connectivity does not automatically imply dispersal, gene flow, recolonization or population persistence. This perspective argues that modelled corridors should be treated as testable hypotheses unless they are supported by independent biological evidence. We propose a tiered claim–evidence framework that distinguishes structural predictions, species-informed hypotheses, demonstrated corridor use and demonstrated conservation outcomes. Field validation need not be universal or identical across studies; its intensity should be proportional to claim strength, spatial scale and decision risk. Moving from one-off mapping toward an adaptive prediction–validation–update cycle would make ecological networks more credible scientific and conservation tools.




