Abstract
Invasive non-native species pose a large threat to restoration efforts following large-scale disturbances. Bromus tectorum (cheatgrass) is a non-native annual grass in the western U.S. that both spreads quickly following fire and accelerates the fire cycle. Herbicide and seeding applications are common restoration practices to break the positive fire-invasion feedback loop and recover native perennial species, but their interactive effects have infrequently been tested at the landscape-scale and repeated in time to encourage long-lasting effects. We determined the efficacy of repeated post-fire application of the herbicide imazapic and seeding treatments to suppress Bromus abundance and promote perennial vegetation recovery. We found that the selective herbicide reduced Bromus cover by ~30 % and density by >50 % across our study sites, but had a strong initial negative effect on seeded species. The most effective treatment to promote perennial seeded species cover was seeding them alone followed by herbicide application 3 years later when the seeded species had established. The efficacy of the treatments was strongly influenced by water availability, as precipitation positively affected the density and cover of Bromus; soil texture and aspect secondarily influenced Bromus abundance and seeded species cover by modifying water retention in this semi-arid region. Warmer temperatures positively affected the non-native annual grass in the cool-season, but negatively affected seeded perennial species in the warm-season, suggesting an important role of seasonality in a region projected to experience large increases in warming in the future. Our results highlight the importance of environmental interactions and repeated treatments in influencing restoration outcomes at the landscape-scale.





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References
Booth MS, Caldwell MM, Stark JM (2003) Overlapping resource use in three Great Basin species: implications for community invasibility and vegetation dynamics. J Ecol 91:36–48
Bradley BA, Mustard JF (2006) Characterizing the landscape dynamics of an invasive plant and risk of invasion using remote sensing. Ecol Appl 16:1132–1147
Brisbin H, Thode A, Brooks M, Weber K (2013) Soil seed bank responses to postfire herbicide and native seeding treatments designed to control Bromus tectorum in a Pinyon–juniper woodland at Zion National Park, USA. Invasive Plant Sci Manag 6:118–129
Brooks ML et al (2004) Effects of invasive alien plants on fire regimes. Bioscience 54:677–688
Chambers JC, Roundy BA, Blank RR, Meyer SE, Whittaker A (2007) What makes Great Basin sagebrush ecosystems invasible by Bromus tectorum? Ecol Monogr 77:117–145
Crawley MJ (2007) Mixed-effects models. In: The R book. Wiley, Chichester, pp 627–660
D’Antonio CM, Vitousek PM (1992) Biological invasions by exotic grasses, the grass/fire cycle, and global change. Annu Rev Ecol Syst 23:63–87
Dale VH et al (2001) Climate change and forest disturbances. Bioscience 51:723–734
Davis MA, Grime JP, Thompson K (2000) Fluctuating resources in plant communities: a general theory of invasibility. J Ecol 88:528–534
DiTomaso JM (2000) Invasive weeds in rangelands: species, impacts, and management. Weed Sci 48:255–265
Duncan CA, Jachetta JJ, Brown ML, Carrithers VF et al (2004) Assessing the economic, environmental, and societal losses from invasive plants on rangeland and wildlands. Weed Technol 18:1411–1416
Elseroad AC, Rudd NT (2011) Can imazapic increase native species abundance in cheatgrass (Bromus tectorum) invaded native plant communities? Rangel Ecol Manag 64:641–648
Evans RA, Young JA (1972) Microsite requirements for establishment of annual rangeland weeds. Weed Sci 4:350–356
Evans RD, Rimer R, Sperry L, Belnap J (2001) Exotic plant invasion alters nitrogen dynamics in an arid grassland. Ecol Appl 22:1301–1310
Floyd ML, Hanna DD, Romme WH (2004) Historical and recent fire regimes in Pinon–juniper woodlands on Mesa Verde, Colorado, USA. For Ecol Manag 198:269–289
Hansen AJ, Piekielek N, Davis C, Haas J et al (2014) Exposure of U.S. national parks to land use and climate change 1900–2100. Ecol Appl 24:484–502
Humphrey LD, Schupp EW (2001) Seed banks of Bromus tectorum-dominated communities in the Great Basin. Western North Am Nat 61:85–92
Knapp PA (1996) Cheatgrass (Bromus tectorum L) dominance in the Great Basin Desert: history, persistence, and influences to human activities. Glob Environ Change 6:37–52
Kulpa SM, Leger EA, Espeland EK, Goergen EM (2012) Postfire seeding and plant community recovery in the Great Basin. Rangel Ecol Manag 65:171–181
Mack RN, Pyke DA (1983) The demography of Bromus tectorum: variation in time and space. J Ecol 71:69–93
Matchett JR, O’Neill A, Brooks M, Decker C, Vollmer J, Deuser C (2009) Reducing fine fuel loads, controlling invasive annual grasses, and manipulating vegetation composition in Zion Canyon, Utah. In: US Geological Survey Final Report for Joint Fire Science Project 05-2-1-13, El Portal, CA
Melgoza G, Nowak RS, Tausch RJ (1990) Soil water exploitation after fire: competition between Bromus tectorum (cheatgrass) and two native species. Oecologia 83:7–13
Menz MHM, Dixon KW, Hobbs RJ (2013) Hurdles and opportunities for landscape-scale restoration. Science 339:526–527
Miller ME, Belnap J, Beatty SW, Reynolds RL (2006) Performance of Bromus tectorum L. in relation to soil properties, water additions, and chemical amendments in calcareous soils of southeastern Utah, USA. Plant Soil 288:1–18
Morris C, Monaco TA, Rigby CW (2009) Variable impacts of imazapic rate on downy brome (Bromus tectorum) and seeded species in two rangeland communities. Invasive Plant Sci Manag 2:110–119
Mortensen VL, Carley JA, Crandall CG, Donaldson Jr. KM, Leishman W (1977) Soil survey of Washington County area, Utah. In: Natural Resources Conservation Service. U.S. Government Printing Office, Washington DC
Munson SM, Lauenroth WK (2014) Controls of vegetation structure and net primary production in restored grasslands. J Appl Ecol 51:988–996
Munson S, Belnap J, Schelz CD, Moran M, Carolin TW (2011) On the brink of change: plant responses to climate on the Colorado Plateau. Ecosphere 2:68
Nakagawa S, Schielzeth H (2013) A general and simple method for obtaining R2 from generalized linear mixed-effects models. Methods Ecol Evol 4:133–142
NPS (2006) Kolob Fire rehabilitation—aerial application of herbicide environmental assessment. National Park Service – Zion National Park, UT
Owen SM, Sieg CH, Gehring CA (2011) Rehabilitating Downy Brome (Bromus tectorum)—invaded shrublands using imazapic and seeding with native shrubs. Invasive Plant Sci Manag 4:223–233
Pinheiro J, Bates D, DebRoy S, Sarkar D, Team RC (2014) nlme: linear and nonlinear mixed effects model. R package version 3.1-117. http://cran.r-project.org/package=nlme
Poesen JW, Lavee H (1994) Rock fragments in top soils: significance and processes. Catena 23:1–28
PRISM (2014) PRISM Climate Group. http://www.prism.oregonstate.edu. Accessed 1 March 2014
Shaner DL, O’Connnor SL (1991) The imidazolinone herbicides. CRC Press, Boca Raton
Shinn SL, Thill DC (2004) Tolerance of several perennial grazzes to imazapic. Weed Technol 18:60–65
Stewart G, Hull AC (1949) Cheatgrass (Bromus tectorum L.)—an ecologic intruder in southern Idaho. Ecology 30:58–74
Thode A, Weber K, Haubensak K, Brisbin H, Brooks M (2010) Treatment effectiveness monitoring for the Kolob Fire burned area rehabilitation treatments. In: Burned Area Emergency Response Report. Flagstaff, AZ, pp 43
Vollmer JL, Vollmer JG (2008) Controlling cheatgrass in winter range to restore habitat and endemic fire. In: Kitchen S, Pendleton RL, Monaco TA, Vernon J (eds) Shrublands under fire: disturbance and recovery in a changing world. USFS Rocky Mountain Research Station, Fort Collins, pp 57–60
Walsh C, Mac Nally R (2013) hier.part: hierarchical partitioning, R package version 1.0-4. http://cran.r-project.org/package=hier.part. Accessed 1 March 2014
Westerling AL, Hidalgo HG, Cayan DR, Swetnam TW (2006) Warmer and earlier spring increase western U.S. forest wildfire activity. Science 313:940–943
Zelikova TJ, Hufbauer RA, Reed SC, Wertin T, Fettig C, Belnap J (2013) Eco-evolutionary responses of Bromus tectorum to climate change: implications for biological invasions. Ecology and Evolution 3:1374–1387
Acknowledgments
This project was supported by funding from the National Park and the U.S. Geological Survey. We thank Linda Kerr, Kristin Legg, and Nate Benson for their support of this project. We also thank seasonal field crews at Zion National Park for taking vegetation measurements, and Matt Van Scoyoc, Jered Hansen, Harland Goldstein, and Jane Zelikova for technical assistance. Author contributions: M.E.M., C.D., and K.A.J. acquired funding and designed the research, K.W. collected the data, S.M.M. and A.L.L. analyzed the data and led the writing, and all authors contributed to the writing. Any use of trade, product, or firm names in this article is for descriptive purposes only and does not imply endorsement by the U.S. Government.
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Munson, S.M., Long, A.L., Decker, C. et al. Repeated landscape-scale treatments following fire suppress a non-native annual grass and promote recovery of native perennial vegetation. Biol Invasions 17, 1915–1926 (2015). https://doi.org/10.1007/s10530-015-0847-x
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DOI: https://doi.org/10.1007/s10530-015-0847-x


