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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Graminoid > SPECIES: Taeniatherum caput-medusae | Medusahead
 

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FIRE ECOLOGY

SPECIES: Taeniatherum caput-medusae | Medusahead

FIRE ECOLOGY OR ADAPTATIONS:


Fire adaptations: | Medusahead Medusahead establishes after fire from the seed bank and from seed dispersed from off-site sources [9,58,90]. Bioassays of burned soil after a rapidly spreading, wind-driven fire in California found viable medusahead fruits within lightly charred litter [9].

Fire regimes: The expansion of exotic annual grasses such as medusahead has substantially increased frequency of fire in the western United States [65]. Medusahead has a fine structure and its herbage dries completely; therefore, its standing dead biomass is extremely flammable. The hazard of wildfire is further increased by considerable litter [39]. Medusahead litter decomposes more slowly than that of most plants [99], therefore making stands of this annual grass a fire hazard [77]. Slow decomposition is a result of its high silica content [71,95]: total ash content of medusahead contains 72 to 89% silica [95]. The long-lasting litter formed by medusahead is easily ignited and burns readily [72]. Invasion can initiate a cycle where a non-native grass colonizes an area and provides the fine fuel necessary for the initiation and propagation of fire. Fires then increase in frequency, area, and possibly severity. Following these grass-fueled fires, non-native grasses recover more rapidly than native species and cause a further increase in fire [26]. Frequent fires destroy the shrub component of the plant community, and potentially part of the bunchgrass community, without destroying "significant" amounts of medusahead seed [72].

The non-native grasses cheatgrass and medusahead have invaded the low sagebrush communities on the volcanic tablelands of northeastern California and northwestern Nevada. When precipitation is adequate, the interspaces between sagebrush plants are completely covered by these invasive grasses. The fine fuels of these plants, and the accumulation of litter of highly siliceous medusahead, create conditions in which fire is easily carried. Negative effects of wildfires in this region include erosion of the thin, coarse-textured, eolian veneer soils [10]. For example, the herbaceous vegetation of a ponderosa pine/Sandberg bluegrass in Modoc County, California, included many other native herbaceous species. After a wildfire, medusahead excluded almost all other understory species [21].

Historically, the Snake River Plains of Idaho was vegetated with shrub-bunchgrass communities. The primary disturbance was patchy stand-replacement fire, occurring every few decades. Fire usually occurred where sagebrush or other shrubs had grown dense, since bunchgrasses did not often provide adequate continuous fuels. With invasion of exotic annuals and increase such as medusahead, historical patterns of postfire succession were altered. Fire-free intervals have been reduced, and shrub-bunchgrass lands are being converted to annual grassland. According to Peters and Bunting [81], "the landscape has become more homogenous, species diversity has decreased, and burns are larger and more continuous."

The range of fire intervals reported for some species that dominate communities in which medusahead occurs are listed below. To learn more about the fire regimes in those communities refer to the FEIS summary for the dominant species, under "Fire Ecology or Adaptations."

Community or Ecosystem Dominant Species Fire Return Interval Range (years)
California chaparral Adenostoma and/or Arctostaphylos spp. < 35 to < 100
sagebrush steppe Artemisia tridentata/Pseudoroegneria spicata 20-70 [79]
basin big sagebrush Artemisia tridentata var. tridentata 12-43 [87]
mountain big sagebrush Artemisia tridentata var. vaseyana 20-60 [3,20]
Wyoming big sagebrush Artemisia tridentata var. wyomingensis 10-70 (40)** [106,111]
blue grama-needle-and-thread grass-western wheatgrass Bouteloua gracilis-Hesperostipa comata-Pascopyrum smithii < 35
cheatgrass Bromus tectorum < 10
California montane chaparral Ceanothus and/or Arctostaphylos spp. 50-100
western juniper Juniperus occidentalis 20-70
Rocky Mountain juniper Juniperus scopulorum < 35
wheatgrass plains grasslands Pascopyrum smithii < 35
pinyon-juniper Pinus-Juniperus spp. < 35 [79]
Rocky Mountain lodgepole pine* Pinus contorta var. latifolia 25-300+ [1,2,86]
Sierra lodgepole pine* Pinus contorta var. murrayana 35-200
Pacific ponderosa pine* Pinus ponderosa var. ponderosa 1-47 [2]
mountain grasslands Pseudoroegneria spicata 3-40 (10)** [1,2]
Rocky Mountain Douglas-fir* Pseudotsuga menziesii var. glauca 25-100 [2]
coastal Douglas-fir* Pseudotsuga menziesii var. menziesii 40-240 [2,75,83]
California mixed evergreen Pseudotsuga menziesii var. m.-Lithocarpus densiflorus-Arbutus m. < 35 [2]
*fire return interval varies widely; trends in variation are noted in the species summary
**(mean)

POSTFIRE REGENERATION STRATEGY [94]:


Ground residual colonizer (on-site, initial community)
Initial off-site colonizer (off-site, initial community)


Related categories for SPECIES: Taeniatherum caput-medusae | Medusahead

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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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