Agree. We just need to be careful that the argument of wild vs native doesn't distract from getting done those things that we do agree on.
So in some watersheds where invasive trout are mostly stocked I think you could say like you did that we can all focus against stocked trout regardless of the reason and native fish can come out on top.
An example would be the section of restored habitat for brook trout in shavers fork WV where stocking was ceased and that addressed the majority of invasive species found at least in the immediate study area from what I understand.
However, as a counter point here is an example where everyone said lets not worry about wild invasive vs. wild native like you suggested and focused on habitat and water quality instead.
Read the abstract below to see what the result was. Alot of time people think if we just focus on everything else( water temp,habitat, water quality) that native trout will do ok. But as this case study shows wild invasive trout can be the dominant limiting impairment and improving habitat can actually help them displace native brook trout. This stream was 12 deg celcius. All the cold clean water in the world couldn’t save a stream that was 96% brook trout and 4% brown trout for the 3150% increase in brown trout after this project done in the name of brook trout.
“ABSTRACT: In 2007-2011, the Wisconsin Department of Natural Resources and the Kiap-TU-Wish Chapter of Trout Unlimited conducted an extensive stream restoration project at Pine Creek, a native brook trout stream in the Driftless Area of Wisconsin. Primary project objectives were to remedy severe stream bank erosion and increase brook trout abundance by 40-50%. The project restored 2.11 stream miles at a cost of $270,000. In 2009, the Pine Creek Restoration Project was recognized by the National Fish Habitat Action Plan as one of 10 national “Waters to Watch”. Key elements of a monitoring program to evaluate project success included physical and biological attributes measured pre- and post-restoration. Physical attributes included stream temperature and habitat (stream width, water depth, water velocity, canopy cover, stream bank height and cover, and stream bed substrate). Biological attributes included macrophytes, macroinvertebrates, and trout. Beneficial project outcomes included: a decrease in stream temperature, a reduction in stream width, greatly reduced stream bank heights and erosion potential, and increases in water depth, stream bank cover, presence of coarse stream bed substrate, and macrophyte presence. Unanticipated project outcomes included: no change in canopy cover, a decrease in water velocity, no significant improvement in macroinvertebrate metrics, and a significant increase in brown trout abundance and decrease in brook trout abundance. Within eight years post-restoration, numbers of brook trout per mile decreased by 70% (3,800 to 1,200), while numbers of brown trout per mile increased by 3,150% (175 to 5,600). A continuation of this trend may lead to the loss of the brook trout fishery. With brook trout being the only native trout species in the Driftless Area, this project highlights the need for appropriate restoration techniques that can protect and enhance brook trout in streams that could be subject to brown trout co-habitation.”