Centaurea beibersteinii (lapsus)
It has been introduced to North America, where it is considered an invasive plant species in much of the western United States and Canada. In 2000, C. maculosa occupied more than 7 million acres (28,000 km2) in the US.
Knapweed is a pioneer species found in recently disturbed sites or openings. Once it has been established at a disturbed site, it continues to spread into the surrounding habitat. This species outcompetes natives through at least three methods:
- A tap root that sucks up water faster than the root systems of its neighbors,
- Quick spread through high seed production, and
- Low palatability, meaning it is less likely to be chosen as food by herbivores. It is also suspected to be allelopathic, releasing a toxin from its roots that stunts the growth of nearby plants of other species.
Its seed is an achene about a quarter of an inch long with a small bristly pappus at the tip which makes the wind its primary means of dispersal. The leaves are a pale grayish-green. They are covered in fine short hairs. First year plants produce a basal rosette, alternate, up to 6 inches (150 mm) long, deeply divided into lobes. It produces a stem in its second year of growth. Stem leaves less lobed progressively getting smaller toward the top. The stem is erect or ascending, slender, hairy and branching, and can grow up to three feet tall. Because cattle prefer the native bunchgrass over Knapweed, overgrazing occurs, increasing the density and range of knapweed infestations. Human disturbance is also a major cause of infestations. Knapweed readily establishes itself and quickly expands in all growth forms in places of human disturbance such as industrial sites, along roadsides,and along sandy riverbanks, and also has the potential to spread into undisturbed natural areas.
Thirteen biological pest control agents have been used against this plant and its cogener, diffuse knapweed, including the moths Agapeta zoegana and Metzneria paucipunctella, the weevils Bangasternus fausti, Larinus obtusus, and Larinus minutus and Cyphocleonus achates, and the fruit flies Chaetorellia acrolophi, Urophora affinis and Urophora quadrifasciata. But in general, biocontrol has not been shown to be effective against C. maculosa. In some instances, root-herbivory on C. maculosa stimulates additional release of catechin, the main allelopathic chemical which the species emits. In addition, moderate levels of herbivory by biocontrol agents can cause compensatory growth.
Prescribed grazing may be an effective means of controlling infestations. All growth forms are nutritious to sheep. High-density infestations can be controlled by fencing in the control area with sheep until the desired level of removal is achieved.
Allelopathy via catechin
C. maculosa roots exude a substance called (-)-catechin, another stereoisomer of catechin, It acts as an herbicide to inhibit competition by a wide range of other plant species. This phytotoxic compound inhibits seed germination and growth in making phosphorus more available in certain soils. It leads to cell death of competing plants by acidification of the cytoplasm. Some natives, such as Gaillardia grandiflora and Lupinus sericeus, are resistant to catechin-induced toxicity. This resistance is conferred by these plants' ability to produce oxalate. Furthermore, native grasses grown in conjunction with oxalate-producing plants benefited from presence of oxalate.
Impact in the North America
Spotted knapweed likely spread to North America in an alfalfa shipment. It was first recorded in Bingen, Klickitat County, Washington in the late 1800s, and by 1980, it had spread to 26 counties in the Pacific Northwest. In the year 2000 it was reported in 45 of the 50 states in the US. Spotted knapweed primarily affects rangelands of the northwest United States and Canada. A 1996 study estimated the direct plus secondary economic impact of spotted knapweed in Montana to be approximately $42 million annually. When spotted knapweed replaces native grasses, soil erosion and surface runoff are increased, depleting precious soil resources.
The common name spotted knapweed most often refers to Centaurea maculosa, however inconsistencies exist in the scientific community. Two cytotypes of the plant exist which have been named as either different species or subspecies. Centaurea maculosa has been used to describe the diploid and tetraploid form, however the diploid form has been called Centaurea stoebe which, having been published before C. maculosa, is the correct name for the species and the tetraploid form Centaurea biebersteinii.
|Wikimedia Commons has media related to Centaurea stoebe.|
- Mauer, T., Russo, M.J., and Evans, M. (2001). Element stewardship abstract for Centaurea maculosa, spotted knapweed. The Nature Conservancy. Retrieved online: 14 July 2007.
- Zouhar, Kris. ((2001, July).). "Centaurea maculosa. In: Fire Effects Information System, [Online]". U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Retrieved January 8, 2010. Check date values in:
- Somers, Paul (2008). A guide to invasive plants in Massachusetts. Massachusetts division of fisheries and wildlife. p. 39.
- DiTomasso, J.M. (2000). "Invasive weeds in rangelands: Species, impacts, and management". Weed Management 48 (2): 255–265.
- Guobis, Thomas Joseph (1980). "LinkImmigration and establishment of Centaurea maculosa Lam. in a central New York limestone quarry". Thesis (M.S.)--State University of New York. College of Environmental Science and Forestry.
- A.C. Blair (2008). "How do biological control and hybridization affect enemy escape?". Biological Control.
- Mueller-Scharer, H.A. & Schroeder, D. (1993). The biological control of Centaurea spp. in North America: do insects solve the problem? Pest. Sci., 37, 343–353.
- Giles C. Thelen (2005). "Insect herbivory stimulates allelopathic exudation by an invasive plant and the suppression of natives". Ecology Letters.
- Callaway, R. M., DeLuca, T. H., & Belliveau, W. M. (1999). "Biological-Control Herbivores May Increase Competitive Ability of the Noxious Weed Centaurea maculosa". Ecology 80 (4): 1196–1201. doi:10.2307/177067.
- Frost, R. A., & Launchbaugh, K. L. (2003). "Prescription Grazing for Rangeland Weed Management: A New Look at an Old Tool.". Rangelands.
- Tiffany L. Weir (2005). "Oxalate contributes to the resistance of Gaillardia grandiflora and Lupinus sericeus to a phytotoxin produced by Centaurea maculosa". Planta.
- Bais HP, Walker TS, Stermitz FR, Hufbauer RA, Vivanco JM (April 2002). "Enantiomeric-dependent phytotoxic and antimicrobial activity of (±)-catechin. A rhizosecreted racemic mixture from spotted knapweed". Plant Physiol. 128 (4): 1173–9. doi:10.1104/pp.011019. PMID 11950966. (Retracted. If this is intentional, please replace
- Roger L. Sheley, James S. Jacobs and Michael F. Carpinelli (April–Jne 1998). "Distribution, Biology, and Management of Diffuse Knapweed (Centaurea diffusa) and Spotted Knapweed (Centaurea maculosa)". Weed Technology 12 (2): 353–362. Check date values in:
- Zouhar, Kris. "Centaurea maculosa". U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory.
- Hirsch, S. A. and J. A. Leitch (1996). ". The affect of knapweed on Montana’s economy". Agricultural Economics.
- John R. Lacey, Clayton B. Marlow and John R. Lane (1989). "Influence of spotted knapweed (centaurea maculosa) on surface runoff and sediment yield". weed technology 3 (4): 627–631.
- Blair, Amy; Nissen, Scott j.; Hufbauer, Ruth A.; Brunk, Galen R. (September 2006). "A Lack of Evidence for an Ecological Role of the Putative Allelochemical (±)-Catechin in Spotted Knapweed". Journal of Chemical Ecology.
- Species Profile- Spotted Knapweed (Centaurea stoebe), National Invasive Species Information Center, United States National Agricultural Library. Lists general information and resources for spotted knapweed
- Spotted Knapweed, Aliens Among Us. Virtual Exhibit of the Virtual Museum of Canada.