“…investigate ecological patterns and theories (Lombardi et al, 2020;Robinson et al, 2014), interactions among native and invasive species (Dugger et al, 2016;Hegel et al, 2019;Osorio et al, 2020), Consequently, while the opportunity to apply multi-species occupancy models will likely increase, data collection procedures may not be at the correct spatial and temporal scales necessary to meet the closure assumption for many species. The simulations presented here emulated camera trapping data and the simulated level for detection was comparable to observed levels of daily detection for several carnivores (Shannon et al, 2014) F I G U R E 1 Proportion of simulations for which the estimates of (a) occupancy for Species A (Ψ A ), (b) occupancy of Species B given Species A was present (Ψ BA ) and occupancy of Species B, given that Species A was absent (Ψ Ba ) when the simulated pattern was independence (i.e., Ψ BA = Ψ Ba ), (c) Ψ BA and Ψ Ba when the simulated pattern was avoidance (i.e., Ψ BA < Ψ Ba ), and (d) Ψ BA and Ψ Ba when the simulated pattern was aggregation (i.e., Ψ BA > Ψ Ba ), was not different from the true simulated level of occupancy (based on 95% confidence intervals) when sites were closed or not closed (i. may be difficult to meet the closure assumption for some species (Mackenzie & Royle, 2005) due to logistical constraints (e.g., limited equipment or personnel) that require sampling to take longer than a period over which closure can be reasonably assumed (e.g., Johnson et al, 2020), or challenges identifying an appropriate spatial scale (e.g., Jornburom et al, 2020). Consequently, the closure assumption is often relaxed with estimates of occupancy from single-species models interpreted as the probability of 'use' (Gould et al, 2019;Mackenzie, 2005a).…”