Centaurea diffusa

From Wikipedia, the free encyclopedia
Jump to: navigation, search
Diffuse Knapweed
Centaurea diffusa1.jpg
Centaurea diffusa in flower
Scientific classification
Kingdom: Plantae
(unranked): Angiosperms
(unranked): Eudicots
(unranked): Asterids
Order: Asterales
Family: Asteraceae
Tribe: Cynareae
Genus: Centaurea
Species: C. diffusa
Binomial name
Centaurea diffusa
Lam., Encycl. Méth. Bot., 1: 675-676, 1785 [1]

Diffuse Knapweed (Centaurea diffusa), also known as White Knapweed or Tumble Knapweed, is a member of the genus Centaurea in the family Asteraceae.

Description[edit]

Diffuse knapweed is an annual or biennial plant, generally growing to between 10 and 60 cm in height. It has a highly branched stem and a large taproot, as well as a basal rosette of leaves with smaller leaves alternating on the upright stems. Flowers are usually white or pink and grow out of urn-shaped heads carried at the tips of the many branches. Diffuse knapweed often assumes a short rosette form for one year, reaching maximum size, then rapidly growing and flowering during the second year. A single plant can produce approximately 18,000 seeds.[1]

Synonyms[edit]

Distribution[edit]

It is native to Asia Minor (Turkey, Syria), the Balkans, (Bulgaria, Greece, Romania), Ukraine, and southern Russia.

An invasive species[edit]

Diffuse knapweed is considered an invasive species in some parts of North America, having established itself in many areas of the continent. C. diffusa was first identified from North America in 1907 when it was found in an alfalfa field in Washington state. The seeds had presumably[citation needed] been transported in an impure alfalfa seed shipment coming from somewhere in the species native range. Now present in at least 19 states in the United States, it has naturalized in all contiguous states west of the Rockies and additionally in Connecticut, Massachusetts, and New Jersey. Portions of western Canada have also been colonized by this plant.

Areas in which diffuse knapweed has been established generally are plains rangelands or forest benchlands. Land that has been recently disturbed—by human or natural processes—is favored for the establishment of diffuse knapweed. It grows in semi-arid and arid environments and seems to favor light, dry, porous soils. Areas with large amounts of shade or high levels of water discourage diffuse knapweed growth.

Dispersion occurs in the following ways:

  • Agriculture – alfalfa contaminated with diffuse knapweed seed can promote the spread of diffuse knapweed;
  • Wildlife – wild animals eating the seeds or transporting the seeds on fur;
  • Wind – seeds blown out of their capsules held on the plant are distributed over a short range, but when dried out the plant may become a tumbleweed, rolling for great distances and releasing seeds along the way;
  • Water – waterways carry seeds in their flow for long distances before depositing them onto a shore where they germinate.

Wind is the primary means by which diffuse knapweed seeds are spread.

Effects[edit]

By 1998 diffuse knapweed had naturalized over 26,640 square kilometres (10,290 sq mi) in the western US, and was increasing its range at a rate of 18% annually.[citation needed] Diffuse knapweed can establish itself in grassland, scrubland and riparian environments.[citation needed] It has little value as feed for livestock, as its thistles can damage the mouth and digestive tract of animals that attempt to feed on it. A study in 1973 concluded that ranches lost approximately US$20/km² (8 cents per acre) of diffuse knapweed due to decreased grazing area.[citation needed] In an agricultural setting, it can greatly reduce crop yield and purity.[citation needed]

Control[edit]

Effective control of diffuse knapweed requires a fusion of well-executed land management, biological control, physical control, chemical control and reestablishment of the native species. Any method of control must ensure that the root is removed or the plant will grow back. Additionally, native plant growth in areas where diffuse knapweed has been removed should be encouraged to prevent reestablishment.

Biological control[edit]

Biological control involves the introduction of organisms, usually natural competitors of the invasive species, into the invaded environment in order to control the invasive species. Since 1970, 12 insects have been released to control diffuse knapweed. Of these 12, 10 have become established, and 4 are widely established (Urophora affinis and Urophora quadrifasciata, the root boring beetle, Sphenoptera jugoslavica, and the weevil Larinus minutus).[3] Research based on simulation models have shown that for biocontrol agents to be effective, they must kill their host, otherwise plants can compensate by having increased seedling survival.[4]

Some of the more commonly utilized biocontrol agents are:

  • Lesser knapweed flower weevil (Larinus minutus). Individuals of this species lay their eggs on the seed heads of both diffuse and spotted knapweed. When the larvae emerge from the eggs, they feed upon the seeds of their host plant. As the females of this species can create from 28 to 130 eggs and each larva can consume an entire seed head, an adequate population of Larinus minutus can devastate entire stands of knapweed. The adult weevils feed upon the stems, branches, leaves and undeveloped flower buds. It is native to Greece and is now found in Montana, Washington, Idaho and Oregon.[5]
  • Knapweed root weevil (Cyphocleonus achates). Knapweed root weevils lay approximately 50 to 70 eggs on either diffuse or spotted knapweed. As the name suggests, the larvae produced burrow into the root where they metamorphose into adult form. At this point, they will tunnel through the root to the surface where they will feed on the leaves of knapweed plants. It is native to Austria, Greece, Hungary and Romania and has been introduced to Idaho, Montana, Washington and Oregon.
  • Yellow-winged knapweed root moth (Agapeta zoegana). This moth with root-mining larvae attacks diffuse and spotted knapweed in parts of the United States where it was introduced to control these plants.
  • Two species of Tephritid flies Urophora affinis and Urophora quadrifasciata.[3] Females lay their eggs on flower buds and larvae form galls on the flower head.[3]

Physical control[edit]

Physical control of diffuse knapweed primarily comprises cutting, digging or burning to remove the plants.

  • Cutting - While cutting the aboveground portion of diffuse knapweed will greatly decrease the spread of seeds, it does not remove the root. With only its root still intact, diffuse knapweed can survive and continue to grow. For a program of cutting to be effective, it must be long-term so that the effect of reduced seed spreading can be realized.
  • Digging - this removes both the portion above ground and the root of diffuse knapweed and has shown to be very effective; if the plant is properly disposed of, it can neither regrow nor spread its seeds. The largest problem with digging knapweed is that it is extremely labor-intensive. Additionally, the recently vacated soil should be planted with a native species to avoid knapweed reintroducing itself in the disturbed soil.
  • Burning - setting fire to a crowd of knapweed, if the fire is sufficiently severe, can successfully destroy the above ground and belowground sections of diffuse knapweed. However, precautions must be taken to first ensure that the fire is properly contained and that a new plant community is established to prevent the reintroduction of diffuse knapweed.

Chemical Control[edit]

Chemical control involves the use of herbicides to control diffuse knapweed. The herbicide Tordon (picloram) is recognized as the most effective, but it is common to use multiple herbicides in order to reduce strain on local grasses. The herbicides 2,4-D, dicamba, and glyphosate are also effective for control. In order to be most effective, it must be applied before the knapweed plants have released their seeds, regardless of which herbicide is used. Ongoing research at the University of Colorado suggests that Tordon treatment does not contribute to long-term reductions of exotic species cover and may contribute to recruitment of other invasive species, such as redstem filaree and Japanese brome, which quickly take the place of herbicide-treated diffuse knapweed.

Human influence on invasion[edit]

One of the first influences humans had on diffuse knapweed was to inadvertently introduce it to North America. Diffuse knapweed has reached a level of coverage in that area that dwarfs its native range.[citation needed]

Diffuse knapweed is known to establish more easily and effectively in recently disturbed environments.[citation needed] Disturbed environments generally present low environmental stress because more resources are available than are being used. These available resources often allow the establishment of an invasion in an ecological community.[citation needed] The concentration of diffuse knapweed in such an area is often linked to the level of soil disturbance.[citation needed] Human disturbances often lead to less species diversity in a community.[citation needed] In turn, less species diversity can lead to unused resources, which allow invasive species to more readily establish.[citation needed] Areas such as fallow land, ditches, rangelands, residential and industrial districts and roadsides are all disturbed habitats where diffuse knapweed frequently establishes.[citation needed] Additionally, the removal of foliage and other ground cover increases the likelihood that seeds will come in contact with the soil and germinate.

The largest impact of humans on diffuse knapweed is certainly due to our efforts in controlling and eradicating its invasive populations. The several methods outlined in the control section represent a small sample of literally hundreds of approaches being tried with varying levels of effectiveness. Besides reducing the spread of diffuse knapweed, we are also providing selective pressure against the individuals that cannot withstand a certain method of control. Selective pressure, given sufficient time, can cause the adaptation or evolution of invasive species such as diffuse knapweed. If an individual diffuse knapweed plant survives control efforts because of a trait it possesses, its progeny will make up a greater portion of the population than the plants that succumbed to the control.

Toward an integrated control strategy[edit]

To successfully control diffuse knapweed, an understanding of the mechanism that allows it to be invasive must be developed. Isolating the reason for its invasiveness would allow control methods designed to specifically target the effectiveness of that mechanism to be developed. Additionally, precautions designed to minimize the invisibility of at-risk environments could be carried out.

Summary[edit]

The success of diffuse knapweed must be attributed to a combination of several mechanisms. Its invasiveness is due to a mix of allelopathy, ERH and superior resource competition.[citation needed] However, the most importance must be attributed to the ERH because diffuse knapweed, while a very effective invasive species in its novel environment, is non-invasive and doesn’t establish monocultures in its native range. It is the differences, biotic and abiotic, between its novel and native surroundings that cause it to be invasive.[citation needed]

To demonstrate that the ERH applies to diffuse knapweed, it is essential to show that the absence of natural enemies has a significant positive effect on its success.[citation needed] One way to show this is to observe the effect of introducing some of diffuse knapweed’s natural enemies into its novel environment. If diffuse knapweed, which generally thrives in its invaded environment, is significantly inhibited through the introduction of natural enemies, it can be concluded that diffuse knapweed is more competitive in the absence of its natural enemies. A recent effort at biocontrol of diffuse knapweed in Idaho’s Camas County effectively reduced 80 square kilometres (20,000 acres) of knapweed to minimal levels through the release of the lesser knapweed flower weevil and the knapweed root weevil. Since both of the insects released are natural competitors of diffuse knapweed, and since this and other similar efforts at biocontrol have been successful, there is significant evidence that diffuse knapweed benefits from the absence of its natural enemies.

Another aspect of diffuse knapweed’s success relies on the effect of its allelopathic chemicals in its novel environment.[citation needed] Although there is still debate concerning the effectiveness of allelopathic chemicals in the field, the evidence of allelopathic effects demonstrated in a laboratory setting and its propensity to establish monocultures support the importance of allelopathy to diffuse knapweed’s success.

Curiously, diffuse knapweed’s allelopathic chemicals were shown to have a deleterious effect on the North American competitors but were beneficial to its native competitors.[citation needed] While diffuse knapweed’s native competitors are able to compete more effectively in the presence of allelopathic chemicals, the novel competitor’s fitness is decreased. This situation provides an example of the effectiveness of the allelopathy mechanism benefiting from the ERH. The increased effectiveness of allelopathic chemicals cause diffuse knapweed to experience less competitive pressure. As a result, diffuse knapweed is able to establish more predominantly in this new area.

Another connection between allelopathy and the ERH is the fact that concentrations of allelopathic chemicals were found to increase when diffuse knapweed was planted in North American soil as opposed to Eurasian soil.[citation needed] This effect is probably due to the absence of unfavorable soil conditions or soil microorganisms that exist in its native environment. As a result, the allelopathic chemicals will be able to reach higher concentrations, spread farther and therefore be more effective. By effecting more neighboring plants, the favorable changes in soil condition contribute to the success of diffuse knapweed.

Besides the advantages that diffuse knapweed gains from the ERH and allelopathy, it also possesses several characteristically invasive traits.[citation needed] One factor leading to the superior resource competition of diffuse knapweed is its ability to exist in drought conditions. This advantage allows diffuse knapweed to devote its resources to competition while its neighbors are conserving resources to survive.[citation needed] The high number of seeds produced by diffuse knapweed is also a common trait of invasive plants.[citation needed] A higher density of knapweed will not only increase the concentration of allelopathic chemicals in the soil but will also restrict the nutrients available to native plants.[citation needed] Unfortunately, very little research has been conducted to determine the relative competitive ability between diffuse knapweed and its novel competitors. However, tests conducted on the effect of diffuse knapweed on North American grasses in the absence on allelopathic chemicals demonstrated that the fitness of these grasses declined in the presence of diffuse knapweed.[citation needed] Regrettably, we cannot decide if diffuse knapweed is, for general purposes, a better competitor from this data alone. Comparisons of the deleterious effects between these and other pairs of competitors to arrive at a conclusion.

Diffuse knapweed is successful in its novel range primarily because the organisms and conditions that prevent it from becoming invasive in its native environment are absent.[citation needed] It follows that the introduction of species from its native habitat would be an effective method of control. However, the introduction of a non-native organism has the potential to result in another invasive species outbreak. Therefore, any method of biological control must be preceded by analysis of possible effects.

References[edit]

  1. ^ Harris, P., and R. Cranston. 1979. An economic evaluation of control methods for diffuse and spotted knapweed in western Canada. Canadian Journal of Plant Science 59:375-382.
  2. ^ In Tutin & alt., Flora Europea
  3. ^ a b c Judith H. Myers (2009). "Successful biological control of diffuse knapweed, Centaurea diffusa, in British Columbia, Canada". Biological Control. 
  4. ^ Myers, J.H., Risley, C., 2000. Why reduced seed production is not necessarily translated into successful biological weed control. In: Spencer, N. (Ed.), Proceedings X. International Symposium Biological Control of Weeds. Montana State University, Bozeman, MO, pp. 569–581.
  5. ^ Groppe, K. 1990. Larinus minutus Gyll. (Coleoptera: Curculionidae), a suitable candidate for the biological control of diffuse and spotted knapweed in North America. In: Final Report C.A.B International Institute of Biological Control. Delemont, Switzerland, p. 30.
  1. Washington State weed info: Diffuse knapweed
  2. Diffuse Knapweed (Centaurea diffusa)
  3. H. G. Baker (1974). Annual Review of Ecology and Systematics 5: 1.
  4. K. Bossick, Wood River Journal. A16 (2004).
  5. R. M. Callaway, W. M. Ridenour (2004). Front Ecol Environment 2 (8): 436.
  6. R. M. Callaway, E. T. Aschehoug (2000). Science 290: 521.
  7. A. T. Carpenter & T. A. Murray. ELEMENT STEWARDSHIP ABSTRACT for Centaurea diffusa Lamarck diffuse knapweed. Online.
  8. C. Chou (1999). Crit. Rev. Plant Sci. 18: 609.
  9. D. R. Clements et al.. Agric Ecosyst Environ (in press, corrected proof).
  10. R. I. Colautti, A. Ricciardi, I. A. Grigorovich, H. J. Maclsaac (2004). Ecology Letters 7: 721.
  11. D. J. Fielding, M. A. Brusven and L. P. Kish (1996). Great Basin Nat. 56: 22.
  12. R. J. Harrod, R. J. Taylor (1995). Northwest Sci. 69: 97.
  13. J. L. Hierro, R. M. Callaway (2003). Plant Soil 256: 29.
  14. J. S. Jacobs, R. L. Sheley (1999). J. Range Manage. 52: 626.
  15. R. M. Keane, M. J. Crawley (2002). Trends in Ecology & Evolution 17: 164.
  16. G. Kiemnec, L. Larson (1991). Weed Technol. 5: 612.
  17. K. Zouhar (2001). Centaurea diffusa. In: Fire Effects Information System, [Online]. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Online.
  18. L. Larson. Centaurea diffusa.
  19. L. Larson, G. Kiemnec (2003). Weed Technol. 17: 79.
  20. J. L. Maron, M. Vila, R. Bommarco, S. Elmendorf and P. Beardsley (2004). Ecol. Monogr. 74: 261.
  21. J. Mizutani (1999). Crit. Rev. Plant Sci. 18: 653.
  22. H. Muller-Scharer, U. Schaffner and T. Steinger (2004). Trends in Ecology & Evolution 19: 417.
  23. M. Palmer, M. Linde and G. X. Pons., Acta Oecol. (in press, corrected proof).
  24. R. D. Powell (1990). J. Ecol. 78: 374.
  25. E. L. Rice (1977). Biochem. Syst. Ecol. 5: 201.
  26. A. K. Sakai, F. W. Allendorf, J. S. Holt, D. M. Lodge, J. Molofsky, K. A. With, S. Baughman, R. J. Cabin, J. D. Cohen, N. C. Ellstrand, D. E. McCauley, P. O’Neil, I. M. Parker, J. N. Thompson, S. G. Weller (2001). Annual Review of Ecology and Systematics 32: 305.
  27. T. R. Seastedt (2003). Weed Science 51: 237.
  28. R. L. Sheley, J. S. Jacobs and M. F. Carpinelli (1998). Weed Technol. 12: 353.
  29. D. J. Thompson, D. G. Stout (1991). Canad. J. Bot. 69: 368.
  30. M. Vila, J. Weiner (2004). Oikos 105: 229
  31. J. M. Vivanco, H. P. Bais, F. R. Stermitz, G. C. Thelen and R. M. Callaway (2004). Ecol. Lett. 7: 285.
  32. L. A. Weston, S. O. Duke (2003). Crit. Rev. Plant Sci. 22: 367.
  33. A. J. Willis, M. B. Thomas and J. H. Lawton (1999). Oecologia 120: 632.
  34. R. Wilson, K. G. Beck and P. Westra (2004). Weed Sci. 52: 418.
  35. D. K. Whaley, G. L. Piper (2004). Environmental News 194.

External links[edit]