Abstract

AbstractThe >2,570,000‐ha Flint Hills ecoregion of Kansas, USA, harbors the largest remaining contiguous tract of tallgrass prairie in North America, a unique system, as the remainder of North America's tallgrass prairie has succumbed to development and conversion. Consequently, the loss and degradation of tallgrass prairie has reduced populations of many North American prairie‐obligate species including the regal fritillary (Speyeria idalia) butterfly. Population abundance and occupied range of regal fritillary have declined >99%, restricting many populations to isolated, remnant patches of tallgrass prairie. Such extensive decline has resulted in consideration of the regal fritillary for protection under the Endangered Species Act. Although it is widely accepted that management practices such as fire, grazing, and haying are necessary to maintain prairie ecosystems, reported responses by regal fritillary to these management regimes have been ambiguous. We tested effects of prescribed fire across short, moderate, and long fire‐return intervals as well as grazing and haying management treatments on regal fritillary density. We also tested the relative influence of habitat characteristics created by these management regimes by measuring density of an obligate host plant (Viola spp.) and canopy cover of woody vegetation, grasses, forbs/ferns, bare ground, and litter. We found density was at least 1.6 times greater in sites burned with a moderate fire‐return interval vs. sites burned with short and long fire‐return intervals. Overall management regardless of fire‐return interval did not have an effect on density. Percent cover of grass had the strongest positive association, while percent cover of woody vegetation had the greatest negative effect on density. Our results indicate that patch‐burning is a viable and perhaps even ideal management strategy for regal fritillary in tallgrass prairie landscapes. Additionally, these results elucidate the importance of fire, particularly when applied at moderate‐return intervals to regal fritillary, and corroborate a growing suite of studies that suggest fire is perhaps not as detrimental to populations of regal fritillary as previously believed.

Highlights

  • Once covering ~67 million ha, native tallgrass prairie communities in the United States have been reduced to approximately 4% of their former range (Samson and Knopf 1994)

  • 2014–2016 in northeastern Kansas, at the Fort Riley Military Reservation (FRMR; Geary and Riley counties) and Konza Prairie Biological Station (KPBS; Riley County; Fig. 1). Both the FRMR and KPBS are located within the northern portion of the Flint Hills physiographic region

  • Survey-wide density estimates produced for the FRMR and KPBS reported regal density to be ~0.53 Æ 0.073 individuals per ha at the FRMR and ~0.52 Æ 0.076 (SE) individuals per ha at the KPBS

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Summary

Introduction

Once covering ~67 million ha, native tallgrass prairie communities in the United States have been reduced to approximately 4% of their former range (Samson and Knopf 1994). Grassland management practices such as prescribed fire, livestock grazing, and haying play critical roles in maintaining native prairie in the absence of ecological drivers that historically shaped them (Samson et al 1998, Fuhlendorf and Engle 2004, Toombs et al 2010). These disturbances are considered necessary for prairies to maintain their open structure, depress invasive species spread, prevent woody encroachment, and promote overall productivity (Vogel 1974, Shuey 1997). Loss or infrequent occurrence of these drivers negatively affects tallgrass prairie ecosystems and disturbance-dependent flora and fauna (Collins 1992, Briggs and Knapp 1995, Fuhlendorf and Engle 2004)

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