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Late-Season Targeted Grazing of Yellow Starthistle (Centaurea solstitialis) with Goats in Idaho

Published online by Cambridge University Press:  20 January 2017

Brianna J. Goehring
Affiliation:
Department of Rangeland Ecology and Management, University of Idaho, Moscow, ID 83844
Karen L. Launchbaugh*
Affiliation:
Department of Rangeland Ecology and Management, University of Idaho, Moscow, ID 83844
Linda M. Wilson
Affiliation:
Invasive Plant Management; British Columbia Ministry of Agriculture and Lands, Abbotsford, BC, Canada V3G2M3
*
Corresponding author's E-mail: [email protected]

Abstract

Yellow starthistle (Centaurea solstitialis) is an exotic winter annual forb that is aggressively invasive and problematic in much of California, Idaho, Oregon, and Washington. Yellow starthistle control is particularly challenging in canyon rangelands where accessibility limits control options. Our objective was to evaluate the effects of late-season targeted goat grazing on yellow starthistle and nontarget grasses and forbs. A 3-yr grazing study was initiated in 2006 on a 380-ha (939 acres) canyon grassland site infested with yellow starthistle near White Bird, ID. Twenty-four paired plots were established, with each pair including a fenced subplot to exclude grazing and a similar-sized adjacent subplot that was grazed. Density of yellow starthistle plants and seedheads was assessed after grazing of each plot in all 3 yr and before grazing in the second and third years. Canopy cover of yellow starthistle, grasses, and forbs also was measured. Grazed subplots had 58% fewer yellow starthistle plants than the ungrazed controls after grazing was applied and 94% fewer seedheads after 3 yr of grazing. Cover of yellow starthistle did not differ between grazed and ungrazed subplots after grazing in 2006, whereas grazing decreased yellow starthistle cover in 2007 and 2008 by about 75%. Goat grazing had little impact on canopy cover of grasses and resident forbs, with the exception of after grazing in 2007 when there was less forb cover in grazed areas compared with ungrazed areas. Late-season (i.e., July to November) targeted goat grazing appears to be an effective way to reduce yellow starthistle plant densities at landscape scales, which creates a large window of opportunity for grazing treatment and flexibility for land and livestock managers.

Type
Research
Copyright
Copyright © Weed Science Society of America 

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References

Literature Cited

Balciunas, J. and Villegas, B. 1999. Two new seed head flies attack yellow starthistle. Calif. Agric 53:811.Google Scholar
Benefield, C. B., DiTomaso, J. M., Kyser, G. B., Orloff, S. B., Churches, K. R., Marcum, D. B., and Nader, G. A. 1999. Success of mowing to control yellow starthistle depends on timing and plant's branching form. Weed Sci 48:255265.Google Scholar
Dillon, C. C. 1967. Exposure may influence grassland establishment. J. Range Manag 20:117118.Google Scholar
DiTomaso, J. M. 2000. Invasive plants in rangelands: species, impacts, and management. Weed Sci 48:255265.Google Scholar
DiTomaso, J. M., Kyser, G. B., and Hastings, M. S. 1999. Prescribed burning for control of yellow starthistle (Centaurea solstitialis) and enhanced native plant diversity. Weed Sci 47:233242.Google Scholar
Duncan, C. A. and Jachetta, J. J. 2005. Introduction. Pages 17. in Duncan, C. A. 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
Enloe, S. F., DiTomaso, J. M., Orloff, S. B., and Drake, D. J. 2004. Soil water dynamics differ among rangeland plant communities dominated by yellow starthistle (Centaurea solstitialis), annual grasses, or perennial grasses. Weed Sci 52:929935.Google Scholar
Gelbard, J. L. and Harrison, S. 2005. Invasibility of roadless grasslands: an experimental study of yellow starthistle. Ecol. Appl 15:15701580.Google Scholar
Goehring, B. J. 2009. The effects of targeted grazing of yellow starthistle by domestic goats in northern Idaho and an examination of seed survival in the ruminant digestive tract. M. S. Thesis. Moscow, ID University of Idaho. 65. http://www.cnr.uidaho.edu/range/GraduateThesesandDissertation/Goehring_2009.pdf. Accessed: May 23, 2009.Google Scholar
Hovde, E. M. 2006. Grazing by cattle and sheep affect yellow starthistle. M. S. Thesis. Moscow, ID University of Idaho. 69. http://www.cnr.uidaho.edu/range/GraduateThesesandDissertation/Hovde_2006.pdf. Accessed: October 24, 2007.Google Scholar
Hurlbert, S. H. 1984. Pseudoreplication and the design of ecological field experiments. Ecol. Monogr 54:187211.Google Scholar
Jacobs, J. S., Sheley, R. L., and Borkowski, J. J. 2006. Integrated management of leafy spurge-infested rangeland. Rangeland Ecol. Manag 59:475482.Google Scholar
Johnson, C. G. Jr and Simon, S. A. 1987. 97101. in. Plant Associations of the Wallowa–Snake Province: Wallowa–Whitman National Forest. U.S. Forest Service, USDA, Report No. R6-ECOL-TP-255A-86.Google Scholar
Joley, D. B., Maddox, D. M., Schoenig, S. E., and Mackey, B. E. 2003. Parameters affecting germinablility and seed bank dynamics in dimorphic achenes of Centaurea solstitialis in California. Can. J. Bot 81:9931007.Google Scholar
Joley, D. B., Maddox, D. M., Supkoff, D. M., and Mayfield, A. 1992. Dynamics of yellow starthistle (Centaurea solstitialis) achenes in the field and laboratory. Weed Sci 40:190194.Google Scholar
Kyser, G. B. and DiTomaso, J. M. 2002. Instability in a grassland community after the control of yellow starthistle (Centaurea solstitialis) with prescribed burning. Weed Sci 50:648657.Google Scholar
Lacey, C. A., Kott, R. W., and Fay, P. L. 1984. Ranchers control leafy spurge. Rangelands 6:202204.Google Scholar
Lacey, J. R., Wallander, R., and Olson-Rutz, K. 1992. Recovery, germinability, and viability of leafy spurge (Euphorbia esula) by sheep. Weed Technol 6:599602.Google Scholar
Maddox, D. M. and Mayfield, A. 1985. Yellow starthistle infestations are on the increase. Calif. Agric 39:1012.Google Scholar
Maddox, D. M., Mayfield, A., and Poritz, N. H. 1985. Distribution of yellow starthistle (Centaurea solstitialis) and Russian knapweed (Centaurea repens). Weed Sci 33:315327.Google Scholar
Olson, B. E., Wallander, R. T., and Lacey, J. R. 1997. Effects of sheep grazing on a spotted knapweed-infested Idaho fescue community. J. Range Manag 50:386390.Google Scholar
Olson, B. E. and Wallander, R. T. 1998. Effect of sheep grazing on a leafy spurge-infested Idaho fescue community. J. Range Manag 51:247252.Google Scholar
Pitcairn, M. J., Woods, D. M., Joley, D. B., Turner, C. E., and Balciunas, J. K. 2000. Population buildup and combined impact of introduced insects on yellow starthistle (Centaurea solstitialis L.) in California. Pages 747751. in Spencer, N. R. ed. Proceedings of the X International Symposium on Biological Control of Weeds. Bozeman, MT Montana State University.Google Scholar
Roché, B. F. Jr, Roché, C. J. T., and Chapman, R. C. 1994. Impacts of grassland habitat on yellow starthistle (Centaurea solstitialis) invasion. Northwest Sci 86:8696.Google Scholar
Roché, C. T. and Thill, D. C. 2001. Biology of common crupina and yellow starthistle, two Mediterranean winter annual invaders in western North America. Weed Sci 49:439447.Google Scholar
SAS Institute 2002. Statistical Analysis System for Windows, Release 9.1 Cary, NC: SAS Institute, Inc.Google Scholar
Steel, R. G. and Torrie, J. H. 1980. Principles and Procedures of Statistics: A Biometrical Approach. 2nd ed. New York, NY McGraw-Hill Book Company.Google Scholar
Thill, D. C., Zamora, D. L., and Kambitsch, D. L. 1986. The germination and viability of excreted common crupina (Crupina vulgaris). Weed Sci 34:237241.Google Scholar
Thomsen, C. D., Williams, W. A., George, M. R., McHenry, W. B., Bell, F. L., and Knight, R. S. 1989. Managing yellow starthistle on rangeland. Calif. Agric 43:47.Google Scholar
Thomsen, C. D., Williams, W. A., Vayssiéres, M., Bell, F. L., and George, M. R. 1993. Controlled grazing on annual grassland decreases yellow starthistle. Calif. Agric 47:3640.Google Scholar
Thomsen, C. D., Vayssiéres, M. P., and Williams, W. A. 1997. Mowing and subclover plantings suppress yellow starthistle. Calif. Agric 51:1520.Google Scholar
Trlica, M. J. 2006. Grass Growth and Response to Grazing. Natural Resource Fact Sheet. No. 6.108. http://www.ext.colostate.edu/pubs/natres/06108.pdf. Accessed: December 28, 2009.Google Scholar
Uygur, S., Smith, L., Uygur, F., Cristofaro, M., and Balciunas, J. 2004. Population densities of yellow starthistle (Centaurea solstitialis) in Turkey. Weed Sci 52:746753.Google Scholar
Wallace, J. M., Wilson, L. M., and Launchbaugh, K. L. 2008. The effect of targeted grazing and biological control on yellow starthistle (Centaurea solstitialis) in canyon grasslands of Idaho. Rangeland Ecol. Manag 61:314320.Google Scholar
Wallander, R. T., Olson, B. E., and Lacey, J. R. 1995. Spotted knapweed seed viability after passing through sheep and mule deer. J. Range Manag 48:145149.Google Scholar
Western Region Climate Center 2008. Idaho Climate Summaries. Grangeville, Idaho (103771) weather station. http://www.wrcc.dri.edu/summary/. Accessed: December 31, 2008.Google Scholar
Williams, S. and Prather, T. 2006. Goats: a tool for controlling spotted knapweed. Journal of Extension.44, Article 5RIB6. http://www.joe.org/joe/2006october/rb6.php. Accessed: May 20, 2009.Google Scholar