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In 2009, new guidance for wildland fire management in the United States expanded the range of strategic options for managers working to reduce the threat of high-severity wildland fire, improve forest health and respond to a changing climate. Markedly, the new guidance provided greater flexibility to manage wildland fires to meet multiple resource objectives. We use Incident Status Summary reports to understand how wildland fire management strategies have differed across the western US in recent years and how management has changed since the 2009 Guidance for Implementation of Federal Wildland Fire Management Policy. When controlling for confounding variation, we found the 2009 Policy Guidance along with other concurrent advances in fire management motivated an estimated 27 to 73% increase in the number of fires managed with expanded strategic options, with only limited evidence of an increase in size or annual area burned. Fire weather captured a manager’s intent and allocation of fire management resources relative to burning conditions, where a manager’s desire and ability to suppress is either complemented by fire weather, at odds with fire weather, or put aside due to other priorities. We highlight opportunities to expand the use of strategic options in fire-adapted forests to improve fuel heterogeneity.

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Context Understanding habitat dynamics is essential for effective conservation as landscapes rapidly change. In a companion paper in this issue, Shirk et al. (2022) introduced an automated habitat monitoring system using Google Earth Engine and applied this framework to develop a dynamic model of Mexican spotted owl (Strix occidentalis lucida) habitat across the southwestern US from 1986 to 2020. Objectives We explored the application of this dynamic model of Mexican spotted owl habitat in the context of the species’ ecology. Methods We evaluated environmental correlates of Mexican spotted owl habitat, assessed potential spatial non-stationarity in habitat selection, estimated long-term trends in habitat by quantifying changes in habitat amount and quality between 1986 and 2020, and evaluated the extent to which habitat changes over the past 35 years have been driven by wildfire. Results Topography and climate appeared to outweigh reflectance-based (vegetation) metrics in describing Mexican spotted owl habitat and habitat selection was non-stationary across modeling sub-regions. Total habitat area for Mexican spotted owls declined by ~ 21% since 1986 (0.6% annually), but trends varied spatially and some even reversed over the past decade. Wildfire was responsible for between 8 and 35% of total habitat loss, depending on the sub-region considered. Conclusions The automated habitat monitoring system allowed trend estimation and accurate assessment of current habitat status for Mexican spotted owls; maps were accurate, spatially detailed, and current. The ability to continually produce accurate maps for large land areas for threatened species such as the Mexican spotted owl facilitates science-based land management on public lands in the southwestern US.

Douglas‐fir dwarf mistletoe (Arceuthobium douglasii) is a prevalent species in southwestern mixed‐conifer forests, affecting host trees by reducing growth and seed production and increasing mortality. Dwarf mistletoe infections can also form witches' brooms, which are profusely branched, dense masses of distorted host branches in the crowns of infected trees. Despite their impact on trees, brooms provide nesting, roosting, and foraging habitat for many wildlife species. To determine whether red squirrels (Tamiasciurus hudsonicus) selected brooms for nesting, foraging, or caching sites, we compared use of brooms in Douglas‐fir (Pseudotsuga menziesii) in mixed‐conifer forests in northern Arizona and New Mexico, USA, in 1998 and 1999. Douglas‐fir brooms are classified into 3 distinct forms based on structure and point of origin on the tree. Type I brooms form from an infection near the terminal end of a branch. Type II brooms form from an infection ≤1 m from the tree trunk (bole); the supporting branch usually grows vertically from the point of infection, parallel to the bole. Type III brooms result from an infection on the bole, creating a dense profusion of branches and often forming a platform. We selected trees of 3 size classes (10–25‐, 26–40‐, >40‐cm dbh) from stands and examined them for signs of red squirrel use (e.g., nesting, food storage). Red squirrels selected Type II and III brooms located closer to the bole and with larger platform size for nesting. They selected Type II and III over Type I brooms for caching and foraging use. Retaining Type II and III brooms that have platforms >700 cm2, volumes >15 m2, and are located 4.5–10 m above ground will retain this habitat element for red squirrels.