Poverty oatgrass has adapted to fire by tillering and establishing from seed after
top-kill [32,34,42].
Fire regimes for plant communities and ecosystems in which poverty oatgrass occurs are summarized below. For further
information regarding fire regimes and fire ecology of communities and ecosystems where poverty oatgrass is found, see the "Fire Ecology and Adaptations" section of the FEIS summary for the plant community or ecosystem dominants listed below.
| Community or Ecosystem |
Dominant Species |
Fire Return Interval Range in Years |
| maple-beech-birch |
Acer-Fagus-Betula |
> 1000 |
| sugar maple |
A. saccharum |
> 1000 |
| sugar maple-basswood |
A. s.-Tilia americana |
> 1000 [5] |
| bluestem prairie |
Andropogon gerardii var. gerardii-Schizachyrium scoparium |
< 10 [5,29] |
| Nebraska sandhills prairie |
A. g. var. paucipilus-Schizachyrium scoparium |
< 10 |
| plains grasslands |
Bouteloua spp. |
< 35 |
| blue grama-buffalo grass |
B. gracilis-Buchloe dactyloides |
< 35 |
| sugarberry-America elm-green ash |
Celtis laevigata-Ulmus americana-Fraxinus pennsylvanica |
< 35 to 200 |
| beech-sugar maple |
Fagus spp.-Acer saccharum |
> 1000 |
| juniper-oak savanna |
Juniperus ashei-Quercus virginiana |
< 35 |
| yellow-poplar |
Liriodendron tulipifera |
< 35 |
| wheatgrass plains grasslands |
Pascopyrum smithii |
< 35 |
| Great Lakes spruce-fir |
Picea-Abies spp. |
35 to > 200 |
| northeastern spruce-fir |
Picea-Abies spp. |
35-200 |
| southeastern spruce-fir |
Picea-Abies spp. |
35 to > 200 [5] |
| Rocky Mountain lodgepole pine* |
Pinus contorta var. latifolia |
25-300+ [1,39] |
| shortleaf pine |
P. echinata |
2-15 |
| shortleaf pine-oak |
P. e.-Quercus spp. |
< 10 |
| longleaf pine-scrub oak |
P. palustris-Quercus spp. |
6-10 [5] |
| red pine (Great Lakes region) |
P. resinosa |
10-200 (10)** [5,17] |
| red-white-jack pine* |
P. r.-P. strobus-P. banksiana |
10-300 [5] |
| pitch pine |
P. rigida |
6-25 [6,24] |
| eastern white pine |
P. strobus |
35-200 |
| eastern white pine-eastern hemlock |
P. s.-Tsuga canadensis |
35-200 |
| eastern white pine-northern red oak-red maple |
P. s.-Quercus rubra-Acer rubrum |
35-200 |
| loblolly-shortleaf pine |
P. taeda-P.echinata |
10 to < 35 |
| Virginia pine-oak |
P.virginiana-Quercus spp. |
10 to < 35 |
| aspen-birch |
Populus tremuloides-Betula papyrifera |
35-200 [5] |
| mountain grasslands |
Pseudoroegneria spicata |
3-40 (10)** [1] |
| 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 |
| 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 |
| little bluestem-grama prairie |
Schizachyrium scoparium-Bouteloua spp. |
< 35 |
| eastern hemlock-yellow birch |
Tsuga canadensis-Betula alleghaniensis |
> 200 |
| elm-ash-cottonwood |
Ulmus-Fraxinus-Populus spp. |
< 35 to 200 [5] |
*fire return interval varies widely; trends in variation are noted in the species summary