Hostname: page-component-848d4c4894-pjpqr Total loading time: 0 Render date: 2024-06-25T17:14:55.540Z Has data issue: false hasContentIssue false
  • English
  • Français

Purple Starthistle (Centaurea calcitrapa) Seed Germination

Published online by Cambridge University Press:  20 January 2017

Michael J. Pitcairn ,
James A. Young ,
Charlie D. Clements  and
Joe Balciunas
Michael J. Pitcairn
Affiliation:
California Department of Food and Agriculture, 3288 Meadowview Road, Sacramento, CA 95832
James A. Young*
Affiliation:
United States Department of Agriculture, Agricultural Research Service, 920 Valley Road, Reno, NV 89512
Charlie D. Clements
Affiliation:
United States Department of Agriculture, Agricultural Research Service, 800 Buchanan Street, Albany, CA 97410
Joe Balciunas
Affiliation:
United States Department of Agriculture, Agricultural Research Service, 800 Buchanan Street, Albany, CA 97410
*
Corresponding author's E-mail: jayoung@scs.unr.edu.
Get access Rights & Permissions [Opens in a new window]

Abstract

Purple starthistle is one of the numerous species of Centaurea that have been accidentally introduced to western North America where most have become pernicious noxious weeds. Purple starthistle is not nearly as widely distributed as its close relative, yellow starthistle, but it is more undesirable because of its growth characteristics and the number, length, and persistence of its spines. Purple starthistle reproduces only by seeds. Knowledge of the seed and seedbed ecology of weeds is important in all suppression strategies and especially for purple starthistle, which has potential biological control agents that suppress seed production. Our purpose was to determine the germination of purple starthistle seeds at a wide range of constant or alternating incubation temperatures from 0 through 40 C. The maximum observed germination ranged from 94 to 100%. Some germination occurred at least 75% or above of the 55 temperature regimes tested. Optimum germination, defined as not less than the maximum observed minus one-half of the confidence interval at the 0.01 level of probability, averaged 88 to 96%. Only one accession of purple starthistle had germination at what we classify as very cold seedbed temperatures. All accessions had near 50% germination at cold seedbed temperatures. Germination was highest at moderate seedbed temperatures and declined at warmer temperatures. The only constant incubation temperature that supported optimum germination was 20 C, and that was for only one accession. The only temperature regime that always supported optimum germination was 15/25 C (15 C for 16 h and 25 C for 8 h in each 24-h period).

Keywords

Purple starthistle, Centaurea calcitrapa L. #3 CENCAyellow starthistle, Centaurea solstitialis L.Invasive weedsseed and seedbed ecology
Type
Research
Information
Weed Technology , Volume 16 , Issue 2 , June 2002 , pp. 452 - 456
Copyright
Copyright © Weed Science Society of America 

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

References

Literature Cited

Evans, R. A., Easi, D. A., Book, D. N., and Young, J. A. 1982. Quadratic response surface analysis of seed germination trials. Weed Sci. 30: 411–416.CrossRefGoogle Scholar
Evans, R. A., Holbo, H. R., Eckert, R. E. Jr., and Young, J. A. 1970. Functional environment of downy brome communities in relation to weed control and revegetation. Weed Sci. 18: 154–162.CrossRefGoogle Scholar
Evans, R. A. and Young, J. A. 1970. Plant litter and establishment of alien annual species in rangeland communities. Weed Sci. 18: 697–703.Google Scholar
Evans, R. A. and Young, J. A. 1972. Microsite requirements for establishment of alien annual species in rangeland communities. Weed Sci. 20: 350–356.Google Scholar
Palmquist, D. E., Evans, R. A., and Young, J. A. 1987. Comparative analysis of temperature response surfaces. In Frasier, G. and Evans, R. A., eds. Seed and Seedbed Ecology of Rangeland Plants. Washington: USDA, Agricultural Research Service. pp. 97–104.Google Scholar
Randall, J. M. 2000. Centaurea calcitrapa . In Bossard, C. C., Randall, J. M., and Hosbovsky, M. C., eds. Invasive Plants of California Wildlands. Berkeley, CA: University of California Press. pp. 94–97.Google Scholar
Robbins, W. W. 1940. Alien Plants Growing Without Cultivation in California. Berkeley, CA: Bull. 637, California Agricultural Experiment Station. 128 p.Google Scholar
Roche, C. T. and Roche, B. F. Jr. 1990. Distribution and amount of four knapweed (Centaurea L.) species in eastern Washington. Northwest Sci. 62: 242–253.Google Scholar
Tutin, T. G., Heywood, V. H., Burges, N. A., Valentine, D. H., Walters, S. M., and Webb, D. A., eds. 1976. Flora Europaea. Cambridge, U.K.: Cambridge University Press. p. 282.Google Scholar
Young, J. A. and Evans, R. A. 1982. Temperature Profiles for Germination of Cool Season Grasses. Oakland, CA: ARR-W-72, USDA, Agricultural Research Service. 92 p.Google Scholar
Young, J. A., Evans, R. A., and Kay, B. L. 1973. Temperature requirements for seed germination in an annual-type rangeland community. Agron. J. 65: 656–659.Google Scholar
Young, J. A., Kay, B. L., George, H., and Evans, R. A. 1980. Germination of three species of Atriplex . Agron. J. 72: 705–709.Google Scholar
Young, J. A., Palmquist, D. E., and Evans, R. A. 1991. Temperature profiles for germination of big sagebrush seeds from native stands. J. Range Manag. 44: 385–390.Google Scholar