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You are here >1Up Info > Wildlife, Animals, and Plants > Plant Species > Forb > SPECIES: Alliaria petiolata | Fringed Onion
 

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FIRE ECOLOGY

SPECIES: Alliaria petiolata | Fringed Onion

FIRE ECOLOGY OR ADAPTATIONS:


Fire Adaptations: Although garlic mustard plants are readily top-killed when exposed to fire, they may ultimately survive by sprouting from the root crown [53,54]. Ecological conditions that permit sprouting are not well understood and it is unclear to what extent resprouted plants are capable of producing viable seed (see Fire Effects section of this summary).

At the population level, garlic mustard may be adapted to perpetuate itself in mixed-severity or low-severity surface fire regimes, although this has not been quantified. Even though individual plants may be killed by fire, postfire conditions may be favorable for rapid population expansion because of increases in the area of disturbed habitat and, depending on the extant community, temporary reductions in interspecific competition. Additionally, garlic mustard seed banks may facilitate rapid recolonization of disturbed areas [14]. For example, 3 consecutive years of prescribed burning in a central Illinois black oak forest, with "hot and fast" with flame lengths to 4 ft. (1.2 m), failed to eradicate garlic mustard populations. This was attributable, in part, to the protection afforded a small number of plants by refugia such as the lee of a downed log or an area of damp litter [54]. The ability of individual plants to escape mortality will depends upon fire severity and the heterogeneity of the fire landscape.

Fire Regimes: Garlic mustard may be found within understory surface, stand-replacement, mixed-severity fire, and nonfire regimes [13]. Because garlic mustard has become established only relatively recently in most areas in North America, and because natural fire regimes have been substantially altered in many of these areas, predicting the response of garlic mustard to any particular fire regime is speculative. In some areas colonized by garlic mustard, estimated mean fire return intervals may be longer than the time in which garlic mustard has been present. As natural areas and preserve managers reintroduce fire into locations where natural and anthropogenic fire has been suppressed in recent times, the response of this and many other species may become better understood. Those who intend to reintroduce fire where it has been absent for a substantial period are encouraged to plan and implement research and monitoring programs and share their findings.

Fire regimes of some of the plant communities in which garlic mustard occurs are summarized below. For further information, see the FEIS summaries of the dominant species listed below.

Community or Ecosystem Dominant Species Fire Return Interval Range (years)
maple-beech-birch Acer-Fagus-Betula > 1000
silver maple-American elm A. saccharinum-Ulmus americana < 35 to 200
sugar maple A. saccharinum > 1000 
sugar maple-basswood A. saccharinum-Tilia americana > 1000 [82]
bluestem prairie Andropogon gerardii var. gerardii-Schizachyrium scoparium < 10 [37,58]
sugarberry-America elm-green ash Celtis laevigata-U. americana- Fraxinus pennsylvanica < 35 to 200 
beech-sugar maple Fagus spp.-A. saccharum > 1000 
black ash Fraxinus nigra < 35 to 200 [82]
tamarack Larix laricina 35-200 [58]
yellow-poplar Liriodendron tulipifera < 35 
eastern white pine-northern red oak-red maple Pinus strobus-Quercus rubra-A. rubrum 35-200 
Virginia pine-oak P. virginiana-Quercus spp. 10 to < 35 
sycamore-sweetgum-American elm Platanus occidentalis-Liquidambar styraciflua-U. americana < 35 to 200 [82]
eastern cottonwood Populus deltoides < 35 to 200 [58]
aspen-birch P. tremuloides-Betula papyrifera 35-200 [21,82]
black cherry-sugar maple Prunus serotina-A. saccharum > 1000
oak-hickory Quercus-Carya spp. < 35
northeastern oak-pine Quercus-Pinus spp. 10 to < 35
southeastern oak-pine Quercus-Pinus spp. < 10 
white oak-black oak-northern red oak Q. alba-Q. velutina-Q. rubra < 35 
northern pin oak Q. ellipsoidalis < 35
bur oak Q. macrocarpa < 10 [82]
oak savanna Q. macrocarpa/Andropogon gerardii-Schizachyrium scoparium 2-14 [58,82]
chestnut oak Q. prinus 3-8 
northern red oak Q. rubra 10 to < 35
post oak-blackjack oak Q. stellata-Q. marilandica < 10 
black oak Q. velutina < 35 [82]
elm-ash-cottonwood Ulmus-Fraxinus-Populus spp. < 35 to 200 [21,82]

POSTFIRE REGENERATION STRATEGY [72]:


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: Alliaria petiolata | Fringed Onion

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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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