Abstract

BackgroundDrastic increases in wildfire size and frequency threaten western North American sagebrush (Artemisia L. spp.) ecosystems. At relatively large spatial scales, wildfire facilitates type conversion of sagebrush-dominated plant communities to monocultures of invasive annual grasses (e.g., Bromus tectorum L.). Annual grasses provide fine fuels that promote fire spread, contributing to a positive grass–fire feedback cycle that affects most sagebrush ecosystems, with expected habitat loss for resident wildlife populations. Greater sage-grouse (Centrocercus urophasianus Bonaparte, 1827) are sagebrush obligate species that are indicators of sagebrush ecosystem function because they rely on different components of sagebrush ecosystems to meet seasonal life history needs. Because wildfire cannot be predicted, chronic impacts of wildfire on sage-grouse populations have been largely limited to correlative studies. Thus, evidence from well-designed experiments is needed to understand the specific mechanisms by which wildfire is detrimental to sage-grouse population dynamics.ResultsFollowing a significant wildfire event in the southwest periphery of sage-grouse range, we implemented a before-after-control-impact study with long-term paired (BACIP) datasets of male sage-grouse surveyed from traditional breeding grounds (leks) within and outside the wildfire boundary. We estimated sage-grouse population rate of change in apparent abundance ( hat{uplambda} ) at burned and unburned areas before and after wildfire and derived BACIP ratios, which provide controlled evidence of wildfire impact. We found that hat{uplambda} at leks within the wildfire boundary decreased approximately 16% relative to leks at control sites. Furthermore, we estimated a 98.5% probability that the observed change in hat{uplambda} could be attributed to the wildfire.ConclusionsWe demonstrated adverse wildfire impacts on sage-grouse population growth using an experimental BACIP design, which disentangled the effect of wildfire disturbance from natural population fluctuations. Our results underscore the importance of active and comprehensive management actions immediately following wildfire (i.e., seeding coupled with planting sagebrush), that might offset short-term impacts of wildfire by timing rapid recovery of sagebrush to meet short-term species’ habitat requirements. Burned leks likely have substantial immediate impacts that may extend beyond wildfire boundaries, especially if critical source habitats are removed. Such impacts could fragment habitat and disrupt connectivity, thereby affecting larger populations and possibly contributing to more widespread declines in sage-grouse populations.

Highlights

  • Drastic increases in wildfire size and frequency threaten western North American sagebrush (Artemisia L. spp.) ecosystems

  • In the sagebrush (Artemisia L. spp.) steppe ecosystem of the Great Basin region of the United States, this phenomenon has been exacerbated by the spread of exotic annual grasses, such as cheatgrass (Bromus tectorum L.; Knapp 1996; Brooks et al 2004; Chambers et al 2014; Brooks et al 2015) and medusahead wildrye (Taeniatherum caput-medusae [L.] Nevski; Young 1992)

  • The altered wildfire regime and associated state transitions of sagebrush to annual grasses in sagebrush steppe ecosystems is a major threat to species, such as the greater sage-grouse (Centrocercus urophasianus, Bonaparte, 1827, hereafter sage-grouse; Nelle et al 2000; US Fish and Wildlife Service 2015; Coates et al 2016), that require intact sagebrush communities for certain life stages

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Summary

Introduction

Drastic increases in wildfire size and frequency threaten western North American sagebrush (Artemisia L. spp.) ecosystems. The existing sagebrush community is slow to regenerate through natural seed dispersal, and many common sagebrush species in the Great Basin do not resprout (Bunting et al 1987; Beck et al 2009) This annual grass–wildfire feedback cycle often results in the elimination of sagebrush on the landscape, promoting replacement by annual grasses (Shultz 2006; Miller et al 2013), and subsequently leading to alternative ecosystem states (Hobbs et al 2006; Shriver et al 2019). Such behavioral rigidity following disturbance events could negatively influence population dynamics (Schroeder and Robb 2003; Carroll et al 2017), whereby historically beneficial behaviors become maladaptive in an altered ecosystem (Battin 2004; Robertson et al 2013; O'Neil et al 2020)

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