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FIRE ECOLOGY

SPECIES: Centaurea diffusa | Diffuse Knapweed

FIRE ECOLOGY OR ADAPTATIONS:


Fire adaptations: Information on the fire ecology and adaptations of diffuse knapweed to fire is lacking in the literature. Diffuse knapweed has a large, perennial taproot that may survive fire if the root crown is not killed. It also produces large quantities of seed that may survive fire.

Fire regimes: Diffuse knapweed occurs primarily in bunchgrass and open ponderosa pine forest community types in the northwestern United States and southern British Columbia. The historical fire regimes of these communities were relatively frequent, low-severity surface fires. Diffuse knapweed did not occur in these communities at the time in which these fire regimes were functioning, but has established since fire exclusion began. It is unclear how this type of fire regime might affect diffuse knapweed populations. It is also unclear how the presence of diffuse knapweed might affect these fire regimes, though it has been observed that closely related species, such as spotted knapweed (see the spotted knapweed summary in FEIS), do not carry fire as readily as grasses [61,134]. If this holds true for diffuse knapweed, dense infestations may change the fire regime by changing the fuel characteristics and reducing the fire return interval at a given site.

The following table provides fire regime intervals for some of the communities in which diffuse knapweed may be found.

Community or Ecosystem Dominant Species Fire Return Interval Range (years)
grand fir Abies grandis 35-200 [7]
sagebrush steppe Artemisia tridentata/Pseudoroegneria spicata 20-70 [75]
basin big sagebrush A. t. var. tridentata 12-43 [92]
mountain big sagebrush A. t. var. vaseyana 15-40 [8,12,62]
Wyoming big sagebrush A. t. var. wyomingensis 10-70 (40**) [124,135]
desert grasslands Bouteloua eriopoda and/or Pleuraphis mutica 5-100 
plains grasslands Bouteloua spp. < 35 
blue grama-needle-and-thread grass-western wheatgrass B. gracilis-Hesperostipa comata-Pascopyrum smithii < 35 
grama-galleta steppe B. g.-Pleuraphis jamesii < 35 to < 100 
cheatgrass Bromus tectorum < 10 
western juniper Juniperus occidentalis 20-70 
Rocky Mountain juniper J. scopulorum < 35 [75]
Engelmann spruce-subalpine fir Picea engelmannii-Abies lasiocarpa 35 to > 200 [7]
pinyon-juniper Pinus-Juniperus spp. < 35 [75]
Rocky Mountain lodgepole pine* P. contorta var. latifolia 25-300+ [6,7,89]
Colorado pinyon P. edulis 10-49 [75]
Jeffrey pine P. jeffreyi 5-30 
western white pine* P. monticola 50-200
Pacific ponderosa pine* P. ponderosa var. ponderosa 1-47 
interior ponderosa pine* P. p. var. scopulorum 2-10 [7]
mountain grasslands Pseudoroegneria spicata 3-40 (10**) [6,7]
Rocky Mountain Douglas-fir* Pseudotsuga menziesii var. glauca 25-100 
California mixed evergreen P. m. var. m.-Lithocarpus densiflorus-Arbutus menziesii < 35 
western redcedar-western hemlock Thuja plicata-Tsuga heterophylla > 200 
mountain hemlock* T. mertensiana 35 to > 200 [7]
*fire return interval varies widely; trends in variation are noted in the species summary
**mean

POSTFIRE REGENERATION STRATEGY [109]:


Caudex/herbaceous root crown, growing points in soil
Ground residual colonizer (on-site, initial community)
Initial off-site colonizer (off-site, initial community)
Secondary colonizer (on-site or off-site seed sources)

Related categories for SPECIES: Centaurea diffusa | Diffuse Knapweed

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Content on this web site is provided for informational purposes only. We accept no responsibility for any loss, injury or inconvenience sustained by any person resulting from information published on this site. We encourage you to verify any critical information with the relevant authorities.

Information Courtesy: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory. Fire Effects Information System

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