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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Shrub > Species: Vaccinium pallidum | Hillside Blueberry
 

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FIRE EFFECTS

SPECIES: Vaccinium pallidum | Hillside Blueberry
IMMEDIATE FIRE EFFECT ON PLANT : Most aboveground stems are presumably killed by fire. However, buds are resistant to heat damage [10]. Brayton and Woodwell [10] observed a "few" surviving aboveground stems after a "heavy burn" in New York. Underground regenerative structures are generally well protected by overlying layers of soil. Postfire mortality is apparently low. DISCUSSION AND QUALIFICATION OF FIRE EFFECT : NO-ENTRY PLANT RESPONSE TO FIRE : Hillside blueberry sprouts readily after fire [10,14] from underground rhizomes, buds located on the root collar, and buds located on portions of surviving aerial stems [10,42]. Surviving buds located nearest the stem apex generally sprout to produce the new shoots [10]. Plants commonly sprout from underground rhizomes after aboveground foliage is consumed by fire. Sprouts often originate from root collar buds after only light damage [42]. Sprouting ability may be reduced by severe damage or by fires at too frequent intervals [10]. After wildfires in white oak-scarlet oak (Quercus coccinea)-pitch pine forests of New Jersey, shoot elongation of hillside blueberry was reduced by "heavy" as compared to "light" burns. However, greater population increases were noted after "heavy" burns. Comparative values were as follows [10]: stems/ m sq burn 117 light 138 heavy Some seedling establishment may occur as birds and mammals transport seed from off-site. However, seedling establishment in most blueberries (Vaccinium spp.) is generally limited to favorable sites in good years. Recovery of hillside blueberry is typically rapid. By the second year after a prescribed fire in a clearcut jack pine stand in northern lower Michigan, plants exhibited significant increases in cover [1]. Hillside blueberry was considered dominant in both burned and unburned stands [1]. Cover was documented as follows [1,2]: 1979 1980 1981 cover freq. cover freq. cover freq. mature jack pine stand 27.2 30.0 -- -- -- -- unburned clearcut 11.3 43.3 20.5 44.0 19.2 44.4 burned clearcut 14.3 34.2 9.0 41.0 19.4 43.9 Although hillside blueberry generally increases after fire, small reductions have been noted on certain sites. Ten to 26 months after a burn in north-central New York, Swan [54] reported average frequencies on unburned plots of 47 percent, whereas the average frequency on burned plots was 36 percent. Similarly, Brown [11] observed relative densities of 37.58 percent on burned sites and 43.92 percent on unburned sites in Rhode Island woodlands. DISCUSSION AND QUALIFICATION OF PLANT RESPONSE : NO-ENTRY FIRE MANAGEMENT CONSIDERATIONS : Prescribed fire: Clones of lowbush blueberries such as hillside blueberry persist for years on undisturbed sites. However, fruit production and overall vigor typically decline with age [52]. Fire has been widely used to rejuvenate decadent clones and improve wildlife habitat [52]. Biomass: Estimates of hillside blueberry biomass in New Jersey Pine Barrens were as follows [6]: (kg/ha) control wildfire wildfire pres. burn pres. burn ---- + 1 162 35 Environmental consideration: Hillside blueberry is able to persist in chestnut-oak woodlands of Pennsylvania adjacent to zinc smelters [31]. Studies in these contaminated communities indicated that many species, normally favored by fire, were weakened by exposure to high soil levels of zinc and did not assume prominence on burned sites. However, hillside blueberry, although also weakened by exposure to soil contaminants, nevertheless increased on burned plots. Percent cover was as follows [31]: burned unburned (sampled 14-15 years after fire) control 7.8 1.2 smelter site 4.7 0.9

Related categories for Species: Vaccinium pallidum | Hillside Blueberry

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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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