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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Shrub > SPECIES: Ceanothus velutinus | Snowbrush Ceanothus
 

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FIRE ECOLOGY

SPECIES: Ceanothus velutinus | Snowbrush Ceanothus

FIRE ECOLOGY OR ADAPTATIONS:


Fuels Contribution: | Snowbrush Ceanothus Snowbrush ceanothus burns "quite hot" [2]. The foliage contains volatile oils that may contribute to fire hazard [284]. Percentage of solvent extractives (waxes, oils, terpenes, and fats) by dry weight found in snowbrush ceanothus fuel is as follows [64]:

Foliage Woody fuel (diameter in inches)
  < 0.25 0.26-0.50 0.51-1.00 > 1.00
18.3 6.0 4.2 3.3 2.6

The foliage extractive heating value for snowbrush ceanothus has been reported at 11,942 Btu per pound [64]. Richards [222] found that the potential rate of spread through snowbrush ceanothus can be expected to increase as the growing season progresses from June 20 to September 10. This expectation is based on an increase in caloric content (from 1,400-2,400 calories/gram) and a decrease in the water content (from 68% to 53%) of green vegetation.

The following table presents information on snowbrush ceanothus fuel loading; the data is based on single-species plots and presented by fuel category [64]:

  Load Foliage Woody fuel (diameter in inches)
< 0.25 0.26-0.50 0.51-1.00 > 1.00
Tons/acre Percent
Plot 1 40.91 5.5 24.4 21.1 49.0 --
Plot 2 38.51 3.1 18.9 30.5 36.5 11.8
Plot 3 22.45 6.0 25.3 33.7 35.0 --

Fire Adaptations: | Snowbrush Ceanothus Snowbrush ceanothus has dormant, ground-stored seed that requires heat treatment to germinate [109,148,168,236]. Snowbrush ceanothus is promoted by fire, regenerating from seed stimulated by fire [63,143,163,201,228]. Where its seeds are present in the soil, snowbrush ceanothus may dominate early seral growth following a "medium or hot" fire [12]. Snowbrush ceanothus also sprouts vigorously from the root crown after fire [201,228,236]. Resprouting may be an adaptation to recurring fires, allowing for rapid growth and recovery [201]. Fire creates conditions more favorable for snowbrush ceanothus growth by removing the overstory [109]. Snowbrush ceanothus shows a marked increase in burned forest areas due to heat scarification of seed, sprouting, and increased light [109,119]. When conifers overtop the shrubfields, snowbrush ceanothus may die out because of reduced light intensities in the forest understory [119,120].

As a nitrogen fixer, snowbrush ceanothus plays an important role in nitrogen reaccumulation following fire [143].

Early seral shrub layers dominated by snowbrush ceanothus form in grand fir/big huckleberry [242], grand fir/Rocky Mountain maple [245,247], Douglas-fir/ninebark [244], Douglas-fir/pinegrass [246,248], Douglas-fir/white spirea [249], and Douglas-fir/Rocky Mountain maple [244] habitat types in response to fire. Dry weather patterns following canopy removal and repeated severe fires are likely to produce persistent seral shrubfields [239,304]. In the northern Rocky Mountains, pure stands of snowbrush ceanothus may form on the south-facing slopes of these shrubfields [239].

Fire Regimes: | Snowbrush Ceanothus  Fire regimes for plant communities and ecosystems in which snowbrush ceanothus occurs are listed below. For further information regarding fire regimes and fire ecology of communities and ecosystems where snowbrush ceanothus is found, see the 'Fire Ecology and Adaptations' section of the FEIS species summary for the plant community or ecosystem dominants listed below.

Community or Ecosystem Dominant Species Fire Return Interval Range (years)
silver fir-Douglas-fir Abies amabilis-Pseudotsuga menziesii var. menziesii > 200 
grand fir Abies grandis 35-200 [9]
California chaparral Adenostoma and/or Arctostaphylos spp. < 35 to < 100 
sagebrush steppe Artemisia tridentata/Pseudoroegneria spicata 20-70 [211]
basin big sagebrush Artemisia tridentata var. tridentata 12-43 [230]
mountain big sagebrush Artemisia tridentata var. vaseyana 15-40 [10,46,188]
Wyoming big sagebrush Artemisia tridentata var. wyomingensis 10-70 (40**) [274,294]
California montane chaparral Ceanothus and/or Arctostaphylos spp. 50-100 [211]
curlleaf mountain-mahogany* Cercocarpus ledifolius 13-1000 [13,233]
mountain-mahogany-Gambel oak scrub Cercocarpus ledifolius-Quercus gambelii < 35 to < 100 
western juniper Juniperus occidentalis 20-70 
Rocky Mountain juniper Juniperus scopulorum < 35
western larch Larix occidentalis 25-100
Engelmann spruce-subalpine fir Picea engelmannii-Abies lasiocarpa 35 to > 200 
blue spruce* Picea pungens 35-200 
pinyon-juniper Pinus-Juniperus spp. < 35 [211]
Rocky Mountain lodgepole pine* Pinus contorta var. latifolia 25-300+ [8,9,227]
Sierra lodgepole pine* Pinus contorta var. murrayana 35-200 [9]
Colorado pinyon Pinus edulis 10-49 [211]
Jeffrey pine Pinus jeffreyi 5-30 
western white pine* Pinus monticola 50-200 
Pacific ponderosa pine* Pinus ponderosa var. ponderosa 1-47
interior ponderosa pine* Pinus ponderosa var. scopulorum 2-10 [9]
quaking aspen (west of the Great Plains) Populus tremuloides 7-120 [9,112,183]
Rocky Mountain Douglas-fir* Pseudotsuga menziesii var. glauca 25-100 [9]
coastal Douglas-fir* Pseudotsuga menziesii var. menziesii 40-240 [9,196,224]
California mixed evergreen Pseudotsuga menziesii var. m.-Lithocarpus densiflorus-Arbutus menziesii < 35
California oakwoods Quercus spp. < 35 
canyon live oak Quercus chrysolepis <35 to 200 
blue oak-foothills pine Quercus douglasii-Pinus sabiniana <35 
Oregon white oak Quercus garryana < 35 [9]
California black oak Quercus kelloggii 5-30 [211
redwood Sequoia sempervirens 5-200 [9,89,260]
western redcedar-western hemlock Thuja plicata-Tsuga heterophylla > 200 
western hemlock-Sitka spruce Tsuga heterophylla-Picea sitchensis > 200 
mountain hemlock* Tsuga mertensiana 35 to > 200 [9]
*fire return interval varies widely; trends in variation are noted in the species summary
**mean

POSTFIRE REGENERATION STRATEGY [258]:


Small shrub, adventitious bud/root crown
Ground residual colonizer (on-site, initial community)

Related categories for SPECIES: Ceanothus velutinus | Snowbrush Ceanothus

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

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