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Downy Brome (Bromus tectorum) Control with Imazapic on Montana Grasslands

Published online by Cambridge University Press:  20 January 2017

Jane Mangold*
Affiliation:
Department of Land Resources and Environmental Sciences, Montana State University, Bozeman, MT, 59717
Hilary Parkinson
Affiliation:
Department of Land Resources and Environmental Sciences, Montana State University, Bozeman, MT, 59717
Celestine Duncan
Affiliation:
Weed Management Services, Helena, MT, 59620
Peter Rice
Affiliation:
Division of Biological Sciences, University of Montana, Missoula, MT, 59812
Ed Davis
Affiliation:
Department of Land Resources and Environmental Sciences, Montana State University, Bozeman, MT, 59717
Fabian Menalled
Affiliation:
Department of Land Resources and Environmental Sciences, Montana State University, Bozeman, MT, 59717
*
Corresponding author's E-mail: [email protected]
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Abstract

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Downy brome is a problematic invasive annual grass throughout western rangeland and has been increasing its abundance, spread, and impacts across Montana during the past several years. In an effort to develop effective management recommendations for control of downy brome on Montana rangeland, we compiled data from 24 trials across the state that investigated efficacy of imazapic (Plateau®, BASF Corporation, Research Triangle Park, NC) applied at various rates and timings and with methylated seed oil (MSO) or a nonionic surfactant (NIS). We ran a mixed-model ANOVA to test for main effects and interactions across application rate (70, 105, 141, 176, and 211 g ai ha−1), application timing (preemergent [PRE], early postemergent [EPOST, one- to two-leaf growth stage], and postemergent [POST, three- to four-leaf growth stage]), and adjuvant (MSO, NIS). Application timing and rate interacted to affect downy brome control (P = 0.0033). PRE imazapic application resulted in the lowest downy brome control (5 to 19%), followed by POST application (25 to 77%) and EPOST application (70 to 95%). Downy brome control remained fairly consistent across rates within application timing. Adjuvant (MSO or NIS) did not affect downy brome control (P = 0.2789). Our data indicate that POST application at 105 to 141 g ai ha−1 provides the most-consistent, short-term control of downy brome. Furthermore, applying imazapic to downy brome seedlings shortly after emergence (one- to two-leaf growth stage) provided better control than applying it to older downy brome seedlings (three- to four-leaf growth stage).

Type
Research
Creative Commons
Creative Common License - CCCreative Common License - BYCreative Common License - NCCreative Common License - SA
This is an Open Access article, distributed under the terms of the Creative Commons Attribution-NonCommercial-ShareAlike licence (http://creativecommons.org/licenses/by-nc-sa/4.0/), which permits non-commercial re-use, distribution, and reproduction in any medium, provided the same Creative Commons license is included and the original work is properly cited.
Copyright
Copyright © Weed Science Society of America

References

Literature Cited

Anonymous, . 2008. Plateau® herbicide product label. BASF Publication No. NVA 2011-04-126-0007. Research Triangle Park, NC BASF. 15 p.Google Scholar
Baker, W. L., Garner, J., and Lyon, P. 2009. Effect of imazapic on cheatgrass and native plants in Wyoming big sagebrush restoration for Gunnison sage-grouse. Nat. Areas J. 29:204209.Google Scholar
Calo, A., Brause, S., and Jones, S. 2012. Integrated treatment with a prescribed burn and postemergent herbicide demonstrates initial success in management cheatgrass in a northern Colorado natural area. Nat. Areas J. 32:300304.Google Scholar
Davies, K. W. and Sheley, R. L. 2011. Promoting native vegetation and diversity in exotic annual grass infestations. Restor. Ecol. 19:159165.Google Scholar
Davison, J. C. and Smith, E. G. 2007. Imazapic provides 2-year control of weedy annuals in a seeded Great Basin fuelbreak. Native Plants J. 8:9195.Google Scholar
Diamond, J. M., Call, C. A., and Devoe, N. 2012. Effects of targeted grazing and prescribed burning on community and seed dynamics of a downy brome (Bromus tectorum)- dominated landscape. Inv. Plant Sci. Manag. 5:259269.Google Scholar
Elseroad, A. C. and Rudd, N. T. 2011. Can imazapic increase native species abundance in cheatgrass (Bromus tectorum) invaded native plant communities? Rangeland Ecol. Manag. 64:641648.Google Scholar
Epanchin-Niell, R., Englin, J., and Nalle, D. 2009. Investing in rangeland restoration in the arid west, USA: countering the effects of an invasive weed on the long-term fire cycle. J. Environ. Manag. 91:370379.Google Scholar
Geier, P. W., Stahlman, P. W., Northam, F. E., Miller, S. D., and Hageman, N. R. 1998. MON 37500 rate and timing affects downy brome (Bromus tectorum) control in winter wheat (Triticum aestivum). Weed Sci. 46:366373.Google Scholar
Grichar, W. J. and Sestak, D. C. 2000. Effects of adjuvants on control of nutsedge (Cyperus esculentus and C. rotundus) by imazapic and imazethapyr. Crop Prot. 19:461465.Google Scholar
Kyser, G. B., DiTomaso, J. M., Doran, M. P., Orloff, S. B., Wilson, R. G., Lancaster, D. L., Lile, D. F., and Porath, M. L. 2007. Control of medusahead (Taeniatherum caput-medusae) and other annual grasses with imazapic. Weed Technol. 21:6675.Google Scholar
Markle, D. M. and Lym, R. G. 2001. Leafy spurge (Euphorbia esula) control and herbage production with imazapic. Weed Technol. 5:474480.Google Scholar
Menalled, F., Mangold, J., and Davis, E. 2008. Cheatgrass: Identification, Biology and Integrated Management. MontGuide. MT200811AG. Bozeman, MT Montana State University Extension.Google Scholar
Meyer, S. E., Quinney, D., Nelson, D. L., and Weaver, J. 2007. Impact of the pathogen Pyrenophora semeniperda on Bromus tectorum seedbank dynamics in North American cold deserts. Weed Technol. 47:5462.Google Scholar
Morris, C., Monaco, T., and Rigby, C. W. 2009. Variable impacts of imazapic rate on downy brome (Bromus tectorum) and seeded species in two rangeland communities. Inv. Plant Sci. Manag. 2:110119.Google Scholar
Owen, S. M., Sieg, C. H., and Gehring, C. A. 2011. Rehabilitating downy brome (Bromus tectorum)—invaded shrublands using imazapic and seeding with native shrubs. Inv. Plant Sci. Manag. 4:223233.Google Scholar
Pinheiro, J., Bates, D., DebRoy, S., and Sarkar, D. 2011. R Development Core Team, nlme: Linear and Nonlinear Mixed Effects Models. Wien, Austria R Foundation for Statistical Computing R package, Version 3.1–102.Google Scholar
Radosevich, S. R., Holt, J. S., and Ghersa, C. M. 2007. Ecology of Weeds and Invasive Plants, 3rd ed. Hoboken, NJ J. Wiley. 454 p.Google Scholar
Rice, P. M. 2005. Downy brome. Pages 147170 in Duncan, C. L. and Clark, J. K., eds. Invasive Plants of Range and Wildlands and Their Environmental, Economic, and Societal Impacts. Lawrence, KS Weed Science Society of America.Google Scholar
Ross, M. A. and Lembi, C. A. 1985. Applied Weed Science. Minneapolis, MN Burgess. 340 p.Google Scholar
Sheley, R. L., Carpinelli, M. F., and Reever-Morghan, K. J. 2007. Effects of imazapic on target and nontarget vegetation during revegetation. Weed Technol. 21:10711081.Google Scholar
Smith, R. G., Maxwell, B. D., Menalled, F. D., and Rew, L. J. 2006. Lessons from agriculture may improve the management of invasive plants in wildland systems. Front. Ecol. Environ. 4:428434.Google Scholar
Stougaard, R. N., Mallory-Smith, C. A., and Mickelson, J. A. 2004. Downy brome (Bromus tectorum) response to imazamox rate and application timing in herbicide-resistant winter wheat. Weed Technol. 18:10431048.Google Scholar
Whitson, T. D. and Koch, D. W. 1998. Control of downy brome (Bromus tectorum) with herbicides and perennial grass competition. Weed Technol. 12:391396.Google Scholar