Investigating resource selection patterns of declining species is critical to developing effective conservation strategies and mitigating negative population trends. We trapped and radio-collared northern bobwhite (Colinus virginianus) and recorded the location of each individual three times per week during the northern bobwhite breeding season (April – September) to infer resource selection by non-brooding adults. We defined 13 vegetation communities with varying fire histories and assessed their relative use via a distance-based logistic regression model within a Bayesian framework. We found reliable evidence that non-brooding northern bobwhite preferred supplemental feed lines, recently burned natural pine stands, one-year rough in shrub/scrub, and one-year rough in hardwood-pine stands. Conversely, we found they avoided one-year rough in natural pine stands, recently burned shrub/scrub, and recently burned hardwood-pine stands. Our data suggest that non-brooding bobwhite’s successional stage preference may vary between vegetation communities within the same study area and adds further evidence to the importance of fire and vegetation interspersion in bobwhite management. Results from our study may be applied to enhance habitat for non-brooding northern bobwhite and potentially increase adult survival, an important metric correlated with bobwhite population growth.

Indirect effects of hunting can lead to changes in population dynamics, which can be caused by trait-mediated effects such as, but not limited to, changes in behavior, reproduction, and physiological responses. Our understanding of the effects of activities associated with hunting such as dog training may incur trait-mediated effects and ultimately indirect effects to wildlife populations are underrepresented. We conducted a two-year study on a high-density wild bobwhite population to identify potential impacts of disturbance caused by spring dog training on survival and reproduction. We recorded 40 total encounters with radio-collared bobwhite, where the lowest seasonal encounter rate was 16.7% of available coveys and the highest was 50%. In 2021, mean survival for the control and treatment groups were 0.41 (95% CrI: 0.33, 0.49) and 0.38 (95% CrI: 0.31, 0.46), respectively. In 2022, mean survival for the control group was 0.45 (95% CrI: 0.38, 0.52) and 0.42 (95% CrI: 0.34, 0.50) for the treatment group. We also found no effect of treatment on fecundity and nest survival was similar for both years for both treatments. The neutral results of our study are likely attributed to low encounter rates. Future studies should focus on public land scenarios where disturbances are more frequent and food resources are likely more limited.