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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Shrub > SPECIES: Vaccinium membranaceum | Big Huckleberry
 

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FIRE CASE STUDIES

SPECIES: Vaccinium membranaceum | Big Huckleberry

1st CASE STUDY:


CASE NAME:


Understory burn - western Montana

REFERENCES:


Miller, Melanie. 1976 [103]
Miller, Melanie. 1977 [104]

FIRE CASE STUDY AUTHORSHIP:


Tirmenstein, D. 1990.

SEASON/SEVERITY CLASSIFICATION:


Spring (May 11 to June 29, 1973)/low
Autumn (September 11 to October 11 1973)/low

STUDY LOCATION:


The study site is located approximately 35 miles (56 km) northeast of Missoula, Montana, in the Lubrecht Experimental Forest.

PREFIRE VEGETATIVE COMMUNITY:


Most of the study area was identified as a Douglas-fir/big huckleberry-kinnikinnick (Pseudotsuga menziesii/Vaccinium membranaceum-Arctostaphylos uva-ursi) habitat type, although several plots were transitional to a Douglas-fir/beargrass (Xerophyllum tenax)-kinnikinnick habitat type stocked by Douglas-fir, western larch (Larix occidentalis), lodgepole pine (Pinus contorta) and scattered ponderosa pine (P. ponderosa). Common shrubs included white spirea (Spirea betulifolia), and fool's huckleberry (Menziesia ferruginea).

TARGET SPECIES PHENOLOGICAL STATE:


Not reported

SITE DESCRIPTION:


Elevation 4,800 feet (1,460 m)
Aspect northwest to northeast
Slope 15 to 45%
Soils sandy, thin, and poorly developed


FIRE DESCRIPTION:


Drip torches were used to ignite strip headfires at 16-foot (5-m) intervals. Dead and down woody fuel loadings averaged 6 to 51 tons per acre (1.4-11.4 kg/m2). Fuel and burning conditions were:

  Spring Fall
Prefire Fuel Weight (kg/m2):     
  0-1/4 inch (0-0.635 cm)  0.7 0.10
  1/4-1 inch (0.635-2.54 cm)  0.14 0.15
  1-3 inch (2.54-7.62 cm)  0.43 0.57
  rotten, > 3 inch (7.62 cm) 5.84 4.10
  sound, > 3 inch  1.11 0.65
  total, > 3 inch 6.95 4.75
  Prefire duff depth (cm) 7.59 5.57
  Prefire dead fuel depth (cm) 16.59 16.15
Prefire herbaceous vegetation weight (kg/m2) 0.09 0.07
Burning Conditions:    
  Windspeed (mph) 2.56 2.64
  Slope (average %) 35 37
  Fuel moisture (%)    
  0-1/4 inch (0-0.635 cm) 10.74 20.38
  1/4-1 inch (0.635-2.54 cm) 11.46 23.24
Soil moisture content (%) 29.09 12.51
Relative humidity (%) 37.44 39.45
Understory foliage moisture (%) 259.00 128.31
Ambient air temperature (°F) 68.56 59.91
Fuel reduction weight (kg/m2)    
  0-1/4 inch (0-0.635 cm) 0.02 0.04
  1/4-1 inch (0.635-2.54 cm)  0.06 0.08
  0-1 inch (0-2.54 cm) 0.09 0.12
  1-3 inch (2.54-7.62 cm) 0.08 0.28
  Total > 3 inch (7.62 cm) 4.38 3.36
  Total fuel reduction 4.63 3.88
Mean duff reduction (cm) 1.74 3.85
Duff reduction (%) 24.41 53.41
Heat release (kcal/sec/m2) 103.07 71.68
Average mineral soil temperature    (°F) 143.56 232.73
Average duff surface temperature    (°F) 252.4 359.27
Average temperature (°F) at 2.5 (cm) below duff surface 191.00 320.27
Average temperature (°F) at 5.0 (cm) below duff surface 163.89 299.27
Average temperature (°F) at 7.5 (cm) below duff surface 141.78 263.91


FIRE EFFECTS ON TARGET SPECIES:


The fire was patchy, and dense big huckleberry stands in forest openings did not burn due to lack of fuels. At the end of the first growing season, big huckleberry stem numbers exceeded prefire levels on all plots. On 33% of the spring-burned plots, big huckleberry stem numbers increased 80 to 120%. On one plot, increases of 900% were noted, although 33% died by the following year.

On fall-burned plots, postburn year 1 stem numbers exceeded prefire levels on only 55% of the plots. The majority of plants sprouted during the 1st growing season, although some additional sprouting occurred during the 2nd year. These later sprouting plants presumably originated from deeper rhizomes. On parts of some fall-burned plots, plant density increased but elsewhere all rhizomes were killed.

Sprouting was primarily related to depth of heat penetration rather than to specific phenological development. Sprouting was common on fall-burned plots where heat penetration was slight. Maximum soil temperatures were recorded on microsites with high fuel concentrations and/or low soil moisture. High soil moisture tended to limit rhizome heating. Influence of moisture level on big huckleberry regeneration was as follows:

  Promote big huckleberry regeneration Inhibit big huckleberry regeneration
lower duff moisture content > 100% < 70%
soil moisture content  > 30% < 19%
large fuel moisture high low


Stem densities were also significantly related to the number of stems present prior to the burn.

FIRE MANAGEMENT IMPLICATIONS:


Fire treatment most beneficial to big huckleberry results in damage to senescent stems but does little damage to rhizomes. These conditions are often met by spring burns that occur when soil and duff are still somewhat moist. Spring burning can increase the density of big huckleberry in Douglas-fir-western larch forests. For optimal increases, burning should not be attempted when the lower duff and soil are dry.

Fall burns generally produce greater heat penetration than spring burns and probability of mortality is increased. Fall burns can effectively reduce big huckleberry, particularly where duff reduction is complete.

2nd CASE STUDY:

CASE NAME:


Sawtooth Huckleberry Field: Competing species removal

REFERENCE:


Minore, Don; Smart A. W.; Dubrasich, M. E. 1979 [111]

FIRE CASE STUDY AUTHORSHIP:


Simonin, Kevin. 2000.

SEASON/SEVERITY CLASSIFICATION:


Cut and Burn:  Autumn/low
Burn:  Autumn/low

STUDY LOCATION:


Experimental plots were established 13 miles west of Mount Adams, Washington.

PREFIRE VEGETATIVE COMMUNITY:


The prefire vegetation community consisted of a big huckleberry (Vaccinium membranaceum) dominated understory followed in dominance by beargrass, lupine (Lupinus spp.) and a minor grass component. Lodgepole pine (Pinus contorta), western white pine (P. monticola), subalpine fir (Abies lasiocarpa), Douglas-fir (Pseudotsuga menziesii), mountain hemlock (Tsuga mertensiana), and Engelmann spruce (Picea engelmannii) made up the invading forest canopy. Forest canopy trees were immature, short and poorly formed, often showing considerable snow damage. Within cut and burn treatments all invading tree species were felled by chainsaw in the 2nd week of August. Lodgepole pine dominated the overstory canopy in the burned treatment followed by western white pine, mountain hemlock, subalpine fir, willow (Salix spp.), Engelmann spruce and Douglas-fir:

  lodgepole pine w. white pine mountain hemlock subalpine fir willow Engelmann spruce Douglas-fir Total overstory
 Average overstory cover 11.8 2.6 1.7 1.3 1.0 0.4 0.3 19.1


TARGET SPECIES PHENOLOGICAL STATE:


Not reported

SITE DESCRIPTION:


Experimental treatments occurred at 4,000 feet (1,219 m) on a gently sloping, west by southwest aspect. Soils were shallow and low in nutrients, with a gravelly coarse texture. Specific soil properties are summarized below:

 Property 0-15 (cm) 16-30 (cm) 31-46 (cm)
pH 5.6  5.6 5.8
CEC* (meq/100 g)  13.19 13.10 11.66
N (%) 0.11 0.07 0.05
P (ppm) 14.00 6.00 3.00
K (ppm) 28.40 16.40 11.20
Ca (meq/100 g) 1.04 0.70 0.39
Mg (meq/100 g) 0.08 0.07 0.05
Na (meq/100 g) 0.02 0.02 0.03
Boron (ppm) 0.22 0.22 0.20
Acetate extractable Fe (ppm) 42.00 53.00 168.00
* CEC (cation exchange capacity)

FIRE DESCRIPTION:



Burns were conducted the first week of October, 5 days after a 4-inch (10 cm) snow that fell on 25 September and then melted. Meteorological measurements at the time of burn were recorded from a weather station 5 miles away at the same elevation:

Average temperature   66 degrees Fahrenheit (19 °C)
Relative Humidity 35%
Wind Dry, east, 7 miles/hour (11 km/hr)


Flamethrowers and diesel fuel were used to initiate burns.

Cut and Burn:
Although slash would not carry fire, plots were burned applying flamethrowers over the entire area. Fine fuels and herbaceous vegetation were consumed.

Burn:
Little understory fuel was present and fire could not be kindled or spread. Diesel fuel and flamethrower were used to deliberately burn herbaceous vegetation and lower tree branches. Fine fuels and herbaceous vegetation were consumed. Coarse fuels and duff were blackened. Most trees were killed immediately; others were severely injured.

FIRE EFFECTS ON TARGET SPECIES:


Cut and Burn: Big huckleberry leaves were consumed with stems blackened but not consumed.

Burn:  Big huckleberry leaves were consumed with a few stems surviving.

Berry production (kg/ha) was severely reduced on both cut and burn, and burn treatments:

  Preburn (1972) 19731 1974 1975 19772
Cut and burn -- 0 0 0.27 0.15
Burn 83.01 0 0.03 1.81 4.90
Control 99.30 0 132.15 137.53 35.06
1 Destroyed by spring frost
2 Majority of berries destroyed by severe August hailstorm

Average overstory cover for 4 postburn growing seasons:

  Big huckleberry Lodgepole pine 1,2 Western white pine 1,2 Total competing species 3
Preburn (1972):        
Cut and Burn -- -- -- --
Burn  18.4 9.7 2.7 65.6
Control 22.1 9.3 4.9 58.8
1973:        
Cut and Burn  4.1 0 0 36.5
Burn 5.7 0.2 0.1 38.9
Control 18.2 * 7.3 4.1 53.5
1974:        
Cut and Burn 8.8 0 0 42.9
Burn 15.1 0.6 0 40.7
Control 22.5 * 6.6 3.0 47.2
1975:        
Cut and Burn 6.7 0 0 23.3
Burn 18.1 0.6 0.1 33.1
Control 22.6 * 8.1 3.8 44.1
1977:        
Cut and Burn  11.6 0.1 0 54.5
Burn 18.8 0.7 0.1 59.4
Control 24.4 5.5 2.4 57.2
1 Major overstory tree species, original reference documents the coverage data for all plant species present.
2 Represents coverage above 3.28 feet (1 m); below was recorded within total competing species coverage.
3 Includes standing trees, tree regeneration, shrubs and herbs
* p<0.05 between control and treatments 


FIRE MANAGEMENT IMPLICATIONS:


Fire treatments most beneficial to big huckleberry occur during relatively moist conditions. Damage to rhizomes is reduced when soil and duff are relatively moist. Burning may increase the density of big huckleberry when conditions conducive to low heat transfer throughout the soil are present.


Related categories for SPECIES: Vaccinium membranaceum | Big Huckleberry

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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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