Understanding and mitigating the impacts of habitat fragmentation due to anthropogenic causes (e.g. logging) on wildlife populations consists of three major components: (1) understanding both historical and current population dynamics, structure and behavior of the species of interest; (2) identifying the role and extent that various human activities and changes in land-use patterns play in causing the resulting population structure; (3) understanding how best to mitigate negative anthropogenic impacts on a given landscape. As pointed out by van Oort, McLellan & Serrouya (2011), in many instances the assumption is made that where humans have fragmented once contiguous habitats, wildlife will inevitably establish a new metapopulation structure for the species. If land and wildlife managers and conservation practitioners begin with the premise that a metapopulation structure is in place before confirming this with data, and if these managers proceed to attempt to mitigate our impacts to putatively ensure and enhance habitat connectivity, landscape permeability and genetic and demographic connectivity, our conservation efforts and funds may be misguided.As a hypothetical example, species X is perceived to have been historically distributed fairly evenly across an intact landscape as a relatively panmictic population. At some point in time a road network is constructed within the once contiguous habitat. As time proceeds, the population begins to decline and the management and conservation community decides that these anthropogenic structures (i.e. roads) have severed habitat connectivity for species X forcing the species into a new metapopulation structure. As a result, the decision is made to spend funds to reduce habitat fragmentation through best management practices that reduce road densities and/or via some mitigating structure(s) (e.g. road crossing structures) to enhance both genetic and demographic connectivity (i.e. rescue effect; Simberloff, 1988;Hanski & Gilpin, 1991;Hanski et al., 1995). In this hypothetical example, behavior studies are even conducted demonstrating that species X would utilize patches of minimum size Y and crossing structures with design parameters A, B and C. Once the identified best management practices are used to reduce fragmentation levels and correctly designed crossing structures constructed, species X still continues in decline ultimately going locally extinct. In this hypothetical example, what was clearly missing was an empirically based, baseline understanding of population structure and behavior before fragmentation of the landscape.In the case of mountain caribou Rangifer tarandus caribou, van Oort et al. (2011) claim that spatial severing of habitat by human activities did not lead to the creation of a metapopulation structure in which natal dispersal (or even breeding dispersal) links subpopulations, because the weak 'innate' ability to disperse continues to prevent metapopulation structuring and associated rescue effects of these small, isolated subpopulations. Did cari...