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Wildlife, Animals, and Plants |
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FIRE EFFECTS
IMMEDIATE FIRE EFFECT ON PLANT:Although experimental evidence is lacking, a single, low-severity fire will probably not kill diffuse knapweed unless it is severe enough to kill the root crown. A low-severity fire will also probably not kill diffuse knapweed seeds stored in the soil. It is unclear what effects a severe fire would have on diffuse knapweed plants and seeds. Research in this area is needed. DISCUSSION AND QUALIFICATION OF FIRE EFFECT:No entry PLANT RESPONSE TO FIRE:Diffuse knapweed may sprout from the root crown and/or establish from seed after fire [85]. It is unclear how diffuse knapweed populations may respond to fire. Reports in the literature are scarce and based primarily on speculation and second-hand information, with little experimental evidence available. It can be assumed that the response of diffuse knapweed to fire will vary with the nature of the prefire plant community, the timing and conditions of the burn, and the conditions of the postfire environment. Harrod and others [40] suggested that fire might reduce the ability of diffuse knapweed to produce seed in the current year, since many bolting stems appeared to be reverted back to a rosette stage after fire. This might allow grasses (which appear to be stimulated by fire) to gain a competitive advantage [40]. A single fire in northern Washington, however, increased the cover and density of both diffuse and spotted knapweed without enhancing desired species [97,99]. Roche and Roche [85] suggest that diffuse knapweed can resprout even after intense wildfire at bolting or flowering stages, although they provide no experimental evidence for this assertion. They further suggest that fire may damage desirable residual species while stimulating knapweed (Centaurea spp.) populations. Reproduction by abundant seed gives diffuse knapweed an advantage in fire-prone environments. Spotted knapweed seeds demonstrate some resistance to high temperatures [1]. This may also be true for diffuse knapweed. Diffuse knapweed seeds may persist in the soil and germinate after fire. Where diffuse knapweed plants are left standing, seeds may be present above ground as well. This "aerial seed bank" may or may not be an advantage after fire, depending upon the characteristics of the fire. Renney and Hughes [84] suggest that burning shows some promise for diffuse knapweed control, especially since the viability of seeds held above ground in the seedhead is considerably reduced by heat, though they give no reference to experimental evidence for this conclusion. Watson [129] notes that seed collected from diffuse knapweed plants in an area burned by a mid-August wildfire was not viable. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE:No entry FIRE MANAGEMENT CONSIDERATIONS:Fire as a control agent: With very few examples in the literature of the effects of fire on diffuse knapweed, it is not surprising to find mixed opinions on the potential effectiveness of fire to control the plant. Control of diffuse knapweed with a single fire is likely to be only temporary [85], because it is a perennial species that produces abundant seed that spreads by tumbleweed action [84]. It is commonly suggested that fire may be used to remove plant debris and improve herbicide efficacy, but again, there is no experimental evidence to support this [22,85]. Others suggest that burning may be an effective means of controlling diffuse knapweed in areas where seasonal or occasional fires are part of the natural ecosystem [16]. Watson and Renney [128] cite Popova (1960) as reporting that fire provides effective control of diffuse knapweed, with vigorous grass regrowth after burning in the Crimea. Additionally, repeated burning of prairie and dune sites in Michigan has proven to encourage growth of native vegetation and reduce spotted knapweed density [61]. Repeated burns may also prevent new seed production and eventually deplete the seed bank. Postfire colonization potential: Diffuse knapweed has the potential to invade an area following fire. Fire provides an ideal seedbed by removing shade and exposing mineral soil. Therefore, if diffuse knapweed was present on or near the site prior to the fire, there is potential for its establishment. It is a good idea to survey the surrounding area for diffuse knapweed skeletons that may contain seed that could be dispersed through tumbleweed action. Diffuse knapweed is 1 of the introduced species mentioned as "taking over large tracts of logged, burned, or otherwise disturbed lands in British Columbia" [119]. The USDA Forest Service's "Guide to Noxious Weed Prevention Practices" [120] provides several fire management considerations for weed prevention in general that apply to diffuse knapweed. Wildfire managers might consider including weed prevention education and providing weed identification aids during fire training; avoiding known weed infestations when locating fire lines, monitoring camps, staging areas, helibases, etc., to be sure they are kept weed free; taking care that equipment is weed free; incorporating weed prevention into fire rehabilitation plans; and acquiring restoration funding. When planning a prescribed burn, inventory the project area and evaluate the cover and phenology of any diffuse knapweed present on or adjacent to the site, and avoid ignition and burning in areas at high risk for diffuse knapweed establishment or spread due to fire effects. Avoid creating soil conditions that promote weed germination and establishment. Discuss weed status and risks in burn rehabilitation plans. To prevent infestation, re-establish vegetation on bare ground as soon after fire as possible, using either natural recovery or artificial techniques as appropriate to site conditions and objectives. When reseeding after wildfires and prescribed burns, use only certified weed-free seed. Monitor the burn site and associated disturbed areas after the fire and the following spring for emergence of diffuse knapweed, and treat to eradicate any emergent diffuse knapweed plants. Regulate human, pack animal, and livestock entry into burned areas at risk for weed invasion until desirable site vegetation has recovered sufficiently to resist weed invasion. Additional guidelines and specific recommendations and requirements are available [120].
Related categories for SPECIES: Centaurea diffusa | Diffuse Knapweed |
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